A.
INTRODUCTION
Competition between plants for the capture of the essential
resources for plant growth (light, water, and nutrients) is a critical process
in natural, semi-natural, and agricultural ecosystems. (Agro)ecologists have
studied interplant competition intensively. However, because of the complex
nature of interplant competition, it has been difficult to develop
generalizing concepts and theories.
In general, a weed is a plant that is considered by the user of
the term to be a nuisance. The word commonly is applied to unwanted plants in
human-controlled settings, especially farm fields and gardens, but also lawns, parks, woods, and other areas. More vaguely,
"weed" is applied to any plants that grow and reproduce aggressively
and invasively. In weed ecology some authorities speak of the
relationship between "the three Ps": plant, place, perception.
Weeds may be unwanted for a number
of reasons. The most important one is that they interfere with food and fiber
production in agriculture, where in
they must be controlled in order to prevent lost or diminished crop yields. The next most important
reason is that they interfere with other cosmetic, decorative, or recreational goals,
such as in lawns, landscape architecture, playing fields, and golf courses.
Although farmers must have recognized competition effects in
their systems as soon as they started to shape ecosystems to meet their needs. Competition
has been regarded as one of the major forces behind the appearance and life
history of plants and the structure and dynamics of plant communities. The term weed in its general sense is a
subjective one, without any classification value, since a plant that is a weed in one context is not
a weed when growing where it belongs or is wanted. Indeed, a number of
"weeds" have been used in gardens or other cultivated-plant settings.
'Volunteer weeds' are crop plants from one year which are growing in the
subsequent crop. Many studies of plant competition have
been directed towards understanding how plants respond to density in
monocultures and how the presence of weeds affects yield in crops.
B.
DISCUSSION
Weeds generally
share similar adaptations that give them
advantages and allow them to proliferate in disturbed environments whose soil
or natural vegetative cover has been damaged. Naturally occurring disturbed
environments include dunes
and other windswept areas with shifting soils, alluvial
flood plains, river banks and deltas,
and areas that are often burned. Since human agricultural practices often mimic
these natural environments where weedy species have evolved, weeds have adapted
to grow and proliferate in human-disturbed areas such as agricultural fields,
lawns, roadsides, and construction sites. The weedy nature of these species
often gives them an advantage over more desirable crop species because they
often grow quickly and reproduce quickly, have seeds
that persist in the soil seed bank
for many years, or have short lifespans with multiple generations in the same
growing season. Perennial weeds often have underground stems that spread out
under the soil surface or, like ground ivy (Glechoma hederacea), have creeping stems
that root and spread out over the ground.
Some plants
become dominant when introduced into new environments because they are freed
from specialist consumers; in what is sometimes called the “natural enemies
hypothesis,” plants freed from these specialist consumers may increase their
competitive ability. In locations were predation and mutual competitive
relationships no longer exist, some plants are able to increase allocation of
resources into growth or reproduction. The weediness of some species that are
introduced into new environments can be caused by the introduction of new
chemicals; sometimes called the "novel weapons hypothesis," these
introduced allelopathyic chemicals, which
indigenous plants are not yet adapted to, may limit the growth of established
plants or the germination and growth of seeds and seedlings. Weeds
interfere by:
1.
competing with the desired plants for the resources
that a plant typically needs, namely, direct sunlight, soil nutrients, water, and (to a lesser
extent) space for growth;
2.
providing hosts and vectors for plant pathogens, giving
them greater opportunity to infect and degrade the quality of the desired
plants;
3.
offering irritation to the skin or digestive tracts of
people or animals, either physical irritation via thorns, prickles, or burs, or
chemical irritation via natural poisons or irritants in the weed.
The process by
which a plant acquires more of the available resources (such as nutrients,
water or light) from the environment without any chemical action on the
surrounding plants is called resource competition.
A
number of eco-physiological models of competition between weeds and crops have
now been produced. Once a crop: weed competition model has been developed to a
level where there is confidence in its predictions, it can be used in different
environments to interpret differences in yield loss due to weeds, to explore
the interactions between crop, weeds, environment and management factors, and
to extrapolate to situations in which there are, so far, no experimental data. Using
sensitivity analyses of the models, we can identify plant traits that confer
greater competitiveness, thus giving direction to crop breeding programmes.
Competition for
light is simulated on the basis of the leaf area of the competing species and
its distribution over the height of the canopy. The absorbed radiation by the
species in relation to plant height is calculated first. Using the CO 2
assimilation light response of individual leaves, the profile of CO 2
assimilation in the canopy is calculated. Integration over height and the day
gives the daily rate of CO 2 assimilation of the species. After subtraction of
losses for maintenance and growth, the daily growth rate in dry matter of the
species is obtained. Effects of drought and nutrients are taken into account by
a simple water and nutrient balance in which the available amounts of soil
moisture and nutrients during the growing Season are tracked. Soil moisture and
nutrients are allocated to the competing species mainly proportional to their
demands.
World wide a 10%
loss of agricultural production can be attributed to the
competitive effect of weeds, in spite of intensive control of weeds in most
agricultural systems. Without weed control, yield losses range from 10 - 100%,
depending on the competitive ability of the crop. Therefore, weed management is
one of the key elements of most agricultural systems. The use and application
of herbicides was one of the main factors enabling intensification of
agriculture in the past decades. However, increasing herbicide resistance in
weeds, the necessity to reduce cost of inputs, and widespread concern about
environmental side effects of herbicides, have resulted in great pressure on
farmers to reduce the use of herbicides. This led to the development of
strategies for integrated weed management based on the use of alternative
methods for weed control and rationalization of herbicide use. Rather than
trying to eradicate weeds from a field, emphasis is on the management of weed populations.
It has been shown that weed control in some crops (like winter wheat) is
generally not needed to reduce yield loss in the current crop, but only to
avoid problems in future crops. The development of such weed management systems
requires thorough quantitative insight in the behaviour of weeds in
agroecosystems and their effects. This involves both insight in crop-weed interactions
within the growing season as well as the dynamics of weed populations over
growing seasons.
Several attempts
have been made to develop weed control advisory systems, using thresholds for
weed control, i.e. the level of weed infestation which can be tolerated based
on specified criteria which are generally based on. A number of concepts for
thresholds for tactical (within season) and strategic (long-term) decision-making
in weed management have been developed. However, the approach has hardly been
used in practice. Besides problems related to accuracy in yield loss
predictions, good quantitative data on the effects of specific weeds in
specific crops are sparse as well as reliable simple assessment methodologies.
The eficacy of
using agronomic practices to manage weed populations will be improved by a
comprehensive understanding of the mechanisms of competition. Mathematical
models to describe the process of plant competition have developed concurrently
with our increasing empirical understanding. The structure of models has reflected
the prevailing approach to weed management. Earlier research was focused on the
calculation of yield loss as a result of weed competition and an empirical
modelling approach. A more recent interest in managing competition, through
increased knowledge of the ecology and biology of competing species, has
resulted in an increase in the use and development of more mechanistic-based
and dynamic population models for weeds. Used as either a tool for research or
as a method for prediction, the mathematical model is an essential and integral
part of the study of plant competition. Crop-weed competition models have been
used extensively for determining the yield loss of crops that result from varying
densities of weeds. In one of the simplest extensions of this approach,
knowledge of crop-weed competition has been combined with herbicide±weed
resource curves to simulate the effects of herbicide use on crop yield and provide
a rudimentary economic evaluation of herbicide treatments.
Aggressive weeds and grasses can invade the lawn and garden, certain methods to get rid of them
may harm the
cultivated plants as well. Herbicides, commonly called weed killers, contain
ingredients formulated to kill vegetation. While some herbicides are safe to
use among flowers, vegetables, and grasses, others may damage the desirable
plants and affect their growth. Weed killers (herbicides) can
save considerable labor in
the yard and garden. Some of these kill plants selectively, so the manager can
control weeds but not injure desirable plants. Others are not selective and may
kill all plants in an area. They must be applied directly to weeds
carefully to avoid damaging nearby plants.
E.
CONCLUSION
Crop-weed models
incorporating competition have had considerable success in describing how the
process of competition affects crop yield and how strategic weed management
decisions impact on weed numbers for a limited range of economically important
species. There is,
however, a need to increase our understanding of the spatial and temporal
variability in model parameters if they are to be used more in a predictive context
and to pull together data for a wide range of weeds and crops.
Exploration of
integrated weed management requires that we understand how weed management
decisions within the crop growing-season affect: (a) the yield of the crop
through competition for resources, and (b) the biodiversity and numbers of
weeds in the current and future crops. Both mechanistic and phenomenological
models have a role to play here. The former include suficient detail of the relationships
between plant traits and the environment to allow exploration of within-season
management decisions on crop yield, while the latter, although not including
such intricate detail, allow exploration of strategic management decisions on
the abundance of weeds through the crop rotation.
Different
herbicides affect different plant systems, resulting in a range of symptoms from
discolored or distorted leaves and stems to a lack of seedling emergence. When landscape
plants come into contact with herbicides, major problems can ensue. Effects may
be mistaken for indications of insect infestation, disease, nutritional
deficiency or environmental disorder. Identify the plant problem before putting
on any pesticide. Herbicides should not
be applied at high temperatures nor on windy days, as these increase the risk
of drift. While there are techniques to alleviate the damage caused
by accidental contact with herbicides, it
is best to avoid incorrect application.
BIBLIOGRAPHY
Anonimb.
2012. Allelopathy. http://en.wikipedia.org/wiki/Allelopathy.
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2012.
Deen,
et al. 2002. An evaluation of four crop : weed
competition models using a common data set. European Weed Research Society. Weed Research 2003 43, 116–129.
Kroph,
et al. 1993. Modelling Crop-Weed Interactions. International
Rice Research Institute. Printed
in Great Britain by BPCC Wheatons Ltd, Exeter. Philippines.
O’Callaghan,
Angela M., Ph.D. 2002. WEED KILLERS -
THEIR EFFECTS ON PLANTS.http://www.unce.unr.edu/publications/factsheets/FS%2000/FS00-19.htm.
Accesed on Sunday, Mei 27th, 2012.
Park, et al. 2003. The Theory and Application
of Plant Competition Models: an Agronomic Perspective. Annals of Botany 92: 741-748.
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