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8 March 2007 Frampton, Dorset: After ten years of commercialisation,
biotech crops have made a significant, positive impact on the global economy
by enhancing farm income; decreasing pesticide spraying and reducing the
environmental footprint associated with pesticide use and soil cultivation,
according to a study released today.
“Since 1996, adoption of biotech crops has
contributed to reducing greenhouse gas emissions from agriculture and
decreased pesticide spraying,” said Graham Brookes, director of PG
Economics, and one of the authors who conducted the study.
“Farmers
in biotech adopting countries have made significant farm income gains over
the last ten years and at the same time, reduced the environmental impact
associated with agricultural practices, benefiting all citizens. These
economic and environmental gains have also been greatest in developing
countries.”
The study, “Global impact of biotech crops:
socio-economic and environmental effects in the first ten years of
commercial use,” reported that biotech crops have resulted in:
- Substantial net economic benefits at the farm
level amounting to $5 billion in 2005 and $27 billion for the ten year
period.
- a reduction in pesticide spraying by 224 million
kg (equivalent to about 40% of the annual volume of pesticide active
ingredient applied to arable crops in the European Union) and as a result,
decreased the environmental impact associated with pesticide use by more
than 15%
- a significant reduction in the release of
greenhouse gas emissions from agriculture by a reduction is pesticide
spaying applications, soil cultivation and facilitation of No-Till and
conservation cultivation, which, in 2005, was equivalent to removing 4
million cars from the roads.
The study was compiled based largely on extensive
analysis of existing farm-level economic impact data on biotech crops and
additional primary analysis of the environmental impact from base data. A
shorter version of the report has been peer reviewed and published in the
Journal of Agrobiotechnology Management and Economics (AgbioForum.
www.agbioforum.org ) - click the
title: Global impact of biotech crops: socio-economic and environmental
effects in the first ten years of commercial use. AgBioForum
AgBioForum
Volume 9 // Number 3 // 2007.
A full manuscript of the report is available - click
the title: Global impact of biotech crops: socio-economic and environmental effects in
the first ten years of commercial use.
The Executive summary is provided below.
PG Economics are independent consultants specialising
in the economic and environmental impact of technology in agriculture.
For more information, contact
by email, telephone fax and post at:
PG Economics Ltd
Wessex Barn, 8 Dorchester Rd, Frampton, Dorset, DT2 9NB
Telephone: +44 (0)1300 321501 Fax: +44 (0)1303 840959
E-mail:
peter.barfoot@bioportfolio.com or
graham.brookes@btinternet.com
This study presents the findings of research into the
global socio-economic and environmental impact of GM crops in the ten years
since they were first commercially planted on a significant area. It
focuses on the farm level economic effects, the environmental impact
resulting from changes in the use of insecticides and herbicides, and the
contribution towards reducing greenhouse gas (GHG) emissions.
Background context
The analysis presented is largely based on the average
performance and impact recorded in different crops. The economic
performance and environmental impact of the technology at the farm level
does, however vary widely, both between and within regions/countries. This
means that the impact of this technology (and any new technology, GM or
otherwise) is subject to variation at the local level. Also the performance
and impact should be considered on a case by case basis in terms of crop and
trait combinations.
Agricultural production systems (how farmers use
different and new technologies and husbandry practices) are dynamic and vary
with time. This analysis seeks to address this issue, wherever possible, by
comparing GM production systems with the most likely conventional
alternative, if GM technology had not been available. This is of particular
relevance to the case of GM herbicide tolerant (GM HT) soybeans, where prior
to the introduction of GM HT technology, production systems were already
switching away from conventional to no/low tillage production (in which the
latter systems make greater use of, and are more reliant on, herbicide-based
weed control systems - the role of GM HT technology in facilitating this
fundamental change in production systems is assessed below).
In addition, the market dynamic impact of GM crop
adoption (on prices) has been incorporated into the analysis by use of
current prices (for each year) for all crops.
Farm income effects
The impact on farm incomes in the GM adopting countries
has been very positive (Table 1). This derives from enhanced productivity
and efficiency gains:
Ø
In 2005, the direct farm income benefit was about $5 billion.
If the additional income arising from second crop soybeans in Argentina is
also taken into consideration,
this income gain rises to $5.6 billion. This is equivalent to having added
between 3.6% and 4.0% to the value of global production of the four main
crops of soybeans, maize, canola and cotton;
Ø
Since 1996, farm incomes have benefited by $24.2 billion ($27
billion inclusive of second crop soybean gains in Argentina);
Ø
The largest gains in farm income have arisen in the soybean
sector, where the additional income generated by GM HT soybeans in 2005 has
been equivalent to adding 7.1% to value of the crop in the GM growing
countries, or adding the equivalent of 6.05% to the value of the global
soybean crop;
Ø
Substantial gains have also arisen in the cotton sector
(through a combination of higher yields and lower costs). In 2005, cotton
farm income levels in the GM adopting countries were higher by $1.9 billion
and since 1996, the sector has benefited from an additional $8.44 billion.
The 2005 income gains are equivalent to adding 13.3% to the value of the
cotton crop in these countries, or 7.3% to the value of total global cotton
production;
Ø
Significant additions to farm incomes have also arisen in the
maize and canola sectors. The combination of GM insect resistant (GM IR)
and herbicide tolerant (GM HT) technology in maize has boosted farm incomes
by over $3.1 billion since 1996. In the North American canola sector an
additional $893 million has been generated.
Table
1: Global farm income
benefits from growing GM crops 1996-2005: million US $
|
Trait |
Increase in farm income 2005 |
Increase in farm income 1996-2005 |
Farm income benefit in 2005 as % of total
value of production of these crops in GM adopting countries |
Farm income benefit in 2005 as % of total
value of global production of these crops |
|
GM herbicide tolerant
soybeans |
2,281 (2,842) |
11,686 (14,417) |
5.72 (7.1) |
4.86 (6.05) |
|
GM herbicide tolerant
maize |
212 |
795 |
0.82 |
0.39 |
|
GM herbicide tolerant
cotton |
166 |
927 |
1.16 |
0.64 |
|
GM herbicide tolerant
canola |
195 |
893 |
9.45 |
1.86 |
|
GM insect resistant
maize |
416 |
2,367 |
1.57 |
0.77 |
|
GM insect resistant
cotton |
1,732 |
7,510 |
12.1 |
6.68 |
|
Others |
25 |
66 |
N/a |
N/a |
|
Totals |
5,027 (5,588) |
24,244 (26,975) |
6.0 (6.7) |
3.6 (4.0) |
Notes: Others = Virus
resistant papaya and squash, rootworm resistant maize, Bracketed figures
include second crop benefits in
Argentina; Totals for the value
shares exclude ‘other crops’ (ie, relate to the 4 main crops of soybeans,
maize, canola and cotton)
Table 2 summarises this information for some of the
main GM adopting countries. This highlights the important farm income
benefit arising from GM HT soybeans in Argentina, GM IR cotton in China and
a range of GM cultivars in the US. It also illustrates the growing level of
farm income benefits being obtained in developing countries such as South
Africa, Paraguay, India and Mexico.
Table
2: GM crop farm income
benefits 1996-2005 selected countries: million US $
|
|
GM HT soybeans |
GM HT maize |
GM HT cotton |
GM HT canola |
GM IR maize |
GM IR cotton |
Total |
|
US |
7,570 |
771 |
919 |
101 |
1,957 |
1,627 |
12,945 |
|
Argentina |
5,197 |
0.2 |
4.0 |
N/a |
159 |
29 |
5,389.2 |
|
Brazil |
1,367 |
N/a |
N/a |
N/a |
N/a |
N/a |
1,367 |
|
Paraguay |
132 |
N/a |
N/a |
N/a |
N/a |
N/a |
132 |
|
Canada |
69 |
24 |
N/a |
792 |
145 |
N/a |
1,031 |
|
South Africa |
2.2 |
0.3 |
0.2 |
N/a |
59 |
14 |
75.7 |
|
China |
N/a |
N/a |
N/a |
N/a |
N/a |
5,168 |
5,168 |
|
India |
N/a |
N/a |
N/a |
N/a |
N/a |
463 |
463 |
|
Australia |
N/a |
N/a |
4.1 |
N/a |
N/a |
150 |
154.1 |
|
Mexico |
N/a |
N/a |
N/a |
N/a |
N/a |
55 |
55 |
|
Philippines |
N/a |
N/a |
N/a |
N/a |
8 |
N/a |
8 |
|
Spain |
N/a |
N/a |
N/a |
N/a |
28 |
N/a |
28 |
Note: Argentine GM HT
soybeans include second crop soybeans benefits. N/a = not applicable
In terms of the division of the economic benefits
obtained by farmers in developing countries relative to farmers in developed
countries, Table 3 shows that in 2005, the majority of the farm income
benefits (55%) have been earned by developing country farmers. The vast
majority of these income gains for developing country farmers have been from
GM IR cotton and GM HT soybeans.
Table
3: GM crop farm income
benefits 2005: developing versus developed countries: million US $
|
|
Developed |
Developing |
% developed |
% developing |
|
GM HT soybeans |
1,183 |
1,658 |
41.6 |
58.4 |
|
GM IR maize |
364 |
53 |
86.5 |
13.5 |
|
GM HT maize |
212 |
0.3 |
99.9 |
0.1 |
|
GM IR cotton |
354 |
1,378 |
20.4 |
79.6 |
|
GM HT cotton |
163 |
3 |
98.4 |
1.6 |
|
GM HT canola |
195 |
0 |
100 |
0 |
|
GM VR papaya and
squash |
25 |
0 |
100 |
0 |
|
Total |
2,496 |
3,092 |
45 |
55 |
Developing countries
include all countries in South America
Cumulatively over the period 1996 to 2005, developing
country farmers have acquired 47% of the total ($27 billion) farm income
benefit.
Examination of the cost farmers pay for accessing GM
technology relative to the total gains derived, Table 4 shows that across
the four main GM crops, the total cost was equal to about 26% of the total
farm income gains. For farmers in developing countries the total cost is
equal to about 13% of total farm income gains, whilst for farmers in
developed countries the cost is about 38% of the total farm income gain.
Table
4: Cost of accessing GM
technology (in % terms) relative to the total farm income benefits 2005
|
|
All farmers |
Developed countries |
Developing countries |
|
GM HT soybeans |
21 |
32 |
10 |
|
GM IR maize |
44 |
43 |
48 |
|
GM HT maize |
38 |
38 |
81 |
|
GM IR cotton |
21 |
41 |
13 |
|
GM HT cotton |
44 |
43 |
65 |
|
GM HT canola |
47 |
47 |
N/a |
|
Total |
26 |
38 |
13 |
N/a = not applicable
As well as these quantifiable impacts on farm
profitability, there have been other important, more intangible impacts (of
an economic nature). Most of these have been important influences for
adoption of the technology. These include:
Herbicide tolerant crops
Ø
Increased management flexibility that comes from a combination
of the ease of use associated with broad-spectrum, post-emergent herbicides
like glyphosate and the increased/longer time window for spraying;
Ø
Compared to conventional crops, where post-emergent herbicide
application may result in ‘knock-back’ (some risk of crop damage from the
herbicide), this problem is less likely to occur in GM HT crops;
Ø
Facilitation of adoption of no/reduced tillage practices with
resultant savings in time and equipment usage (see below for environmental
benefits);
Ø
Improved weed control has reduced harvesting costs – cleaner
crops have resulted in reduced times for harvesting. It has also improved
harvest quality and led to higher levels of quality price bonuses in some
regions;
Ø
Elimination of potential damage caused by soil-incorporated
residual herbicides in follow-on crops.
Insect resistant crops
Ø
Production risk management/insurance purposes – taking away
the worry of significant pest damage occurring;
Ø
A ‘convenience’ benefit (less time spent on crop walking
and/or applying insecticides);
Ø
Savings in energy use – mainly associated with less spraying;
Ø
Savings in machinery use (for spraying and possibly reduced
harvesting times);
Ø
Improved quality (eg, lower levels of mycotoxins in GM IR
maize);
Ø
Improved health and safety for farmers and farm workers (from
reduced handling and use of pesticides);
Ø
Shorter growing season (eg, for some cotton growers in India)
which allows some farmers to plant a second crop in the same season.
Also some Indian cotton growers have reported knock on benefits for bee
keepers as fewer bees are now lost to insecticide spraying.
In relation to the nature and size of GM technology
adopters, there is clear evidence that size of farm has not been a factor
affecting use of the technology. Both large and small farmers have adopted
GM crops. Size of operation has not been a barrier to adoption. In 2005,
8.5 million farmers were using the technology globally, 90% plus of which
were resource-poor farmers in developing countries.
The significant productivity and farm income gains
identified above have, in some countries (notably Argentina) also made
important contributions to income and employment generation in the wider
economy. For example, in Argentina, the economic gains resulting from the
140% increase in the soybean area since 1995 are estimated to have
contributed towards the creation of 200,000 additional agricultural related
jobs
and export-led economic growth.
Environmental impact from changes in insecticide and
herbicide use
To examine this impact, the study has analysed both
active ingredient use and utilised the indicator known as the Environmental
Impact Quotient (EIQ) to assess the broader impact on the environment (plus
impact on animal and human health). The EIQ distils the various
environmental and health impacts of individual pesticides in different GM
and conventional production systems into a single ‘field value per hectare’
and draws on all of the key toxicity and environmental exposure data related
to individual products. It therefore provides a consistent and fairly
comprehensive measure to contrast and compare the impact of various
pesticides on the environment and human health. Readers should however note
that the EIQ is an indicator only and does not take into account all
environmental issues and impacts. In the analysis of GM HT technology we
have assumed that the conventional alternative delivers the same level of
weed control as occurs in the GM HT production system.
Table 5 summarises the environmental impact over the
last ten years and shows that there have been important environmental gains
associated with adoption of GM technology. More specifically:
Ø
There has been a 15.3% net reduction in the environmental
impact
on the cropping area devoted to GM crops since 1996. The total volume of
active ingredient (ai) applied to crops has also fallen by 7%;
Ø
In absolute terms, since 1996, the largest environmental gains
have arisen from the adoption of GM HT soybeans. This mainly reflects the
(large) share of global GM crop plantings accounted for by GM HT soybeans.
The volume of herbicide use is 4.1% lower and the environmental impact 20%
lower than levels that would have probably arisen if all of this GM crop
area had been planted to conventional cultivars. Readers should note that
in some countries (notably in South America), the adoption of GM HT
technology in soybeans has also coincided with increases in the volume of
herbicides used and the environmental impact relative to historic levels.
As indicated above, this largely reflects the facilitating role of the GM HT
technology in accelerating and maintaining the switch away from conventional
tillage to no/low tillage production systems with their inherent
environmental benefits. This net increase in the environmental impact
should, therefore be placed in the context of the reduced GHG emissions
arising from this production system change (see below) and the general
dynamics of agricultural production system changes (which the analysis
presented above and in Table 5 takes account of);
Ø
Major environmental gains have also been derived from the
adoption of GM insect resistant (IR) cotton (the largest gains on a per
hectare basis). Since 1996, there has been a 24% reduction in the
environmental impact, and a 19% decrease in the volume of insecticides
applied;
Ø
Important environmental gains have also arisen in the maize
and canola sectors. In the maize sector a 4.6% reduction in the
environmental impact has occurred from reduced insecticide use and a switch
to more environmentally benign herbicides has resulted in a further 4%
reduction in the environmental impact of maize herbicides. In the canola
sector, the environmental impact has fallen by 23% because of a switch to
more environmentally benign herbicides.
Table
5: Impact of changes in
the use of herbicides and insecticides from growing GM crops globally
1996-2005
|
Trait |
Change in volume of active ingredient used
(million kg) |
Change in field EIQ impact (in terms of
million field EIQ/ha units) |
% change in ai use in GM growing countries |
% change in environmental impact in GM
growing countries |
|
GM herbicide tolerant
soybeans |
-51.4 |
-4,865 |
-4.1 |
-20.0 |
|
GM herbicide tolerant
maize |
-36.5 |
-845 |
-3.4 |
-4.0 |
|
GM herbicide tolerant
cotton |
-28.6 |
-1,166 |
-15.1 |
-22.7 |
|
GM herbicide tolerant
canola |
-6.3 |
-310 |
-11.1 |
-22.6 |
|
GM insect resistant
maize |
-7.0 |
-403 |
-4.1 |
-4.6 |
|
GM insect resistant
cotton |
-94.5 |
-4,670 |
-19.4 |
-24.3 |
|
Totals |
-224.3 |
-12,259 |
-6.9 |
-15.3 |
The impact of changes in insecticide and herbicide use
at the country level (for the main GM adopting countries) is summarised in
Table 6.
Table
6: Reduction in
environmental impact from changes in pesticide use associated with GM crop
adoption by country 1996-2005 selected countries: % reduction in field EIQ
values
|
|
GM HT soybeans |
GM HT maize |
GM HT cotton |
GM HT canola |
GM IR maize |
GM IR cotton |
|
US |
29 |
4 |
24 |
38 |
5 |
23 |
|
Argentina |
21 |
NDA |
NDA |
N/a |
0 |
4 |
|
Brazil |
6 |
N/a |
N/a |
N/a |
N/a |
N/a |
|
Paraguay |
13 |
N/a |
N/a |
N/a |
N/a |
N/a |
|
Canada |
9 |
5 |
N/a |
22 |
NDA |
N/a |
|
South Africa |
7 |
0.44 |
6 |
N/a |
2 |
NDA |
|
China |
N/a |
N/a |
N/a |
N/a |
N/a |
28 |
|
India |
N/a |
N/a |
N/a |
N/a |
N/a |
3 |
|
Australia |
N/a |
N/a |
4 |
N/a |
N/a |
22 |
|
Mexico |
N/a |
N/a |
N/a |
N/a |
N/a |
NDA |
|
Spain |
N/a |
N/a |
N/a |
N/a |
30 |
N/a |
Note: N/a = not
applicable, NDA = No data available. Zero impact for GM IR maize in
Argentina is due to the negligible
(historic) use of insecticides on the Argentine maize crop
In terms of the division of the environmental benefits
associated with less insecticide and herbicide use for farmers in developing
countries relative to farmers in developed countries, Table 7 shows that in
2005, the majority of the environmental benefits associated with lower
insecticide and herbicide use have been for developing country farmers. The
vast majority of these environmental gains have been from the use of GM IR
cotton and GM HT soybeans
Table
7: GM crop environmental
benefits from lower insecticide and herbicide use 2005: developing versus
developed countries
|
|
% of total reduction in environmental
impact: developed countries |
% of total reduction in environmental
impact: developing countries |
|
GM HT soybeans |
53 |
47 |
|
GM IR maize |
92 |
8 |
|
GM HT maize |
99 |
1 |
|
GM IR cotton |
15 |
85 |
|
GM HT cotton |
99 |
1 |
|
GM HT canola |
100 |
0 |
|
Total |
46 |
54 |
Developing countries
include all countries in South America
Cumulatively over the period 1996 to 2005, developing
country farmers have acquired 48% of the total environmental benefits from
lower insecticide and herbicide use.
Impact on greenhouse gas (GHG) emissions
The scope for GM crops contributing to lower levels of
GHG emissions comes from two principle sources:
Ø
Reduced fuel use from less frequent herbicide or insecticide
applications and a reduction in the energy use in soil cultivation. The
fuel savings associated with making fewer spray runs (relative to
conventional crops) and the switch to conservation, reduced and no-till
farming systems, have resulted in permanent savings in carbon dioxide
emissions. In 2005 this amounted to about 962 million kg (arising from
reduced fuel use of 356 million litres). Over the period 1996 to 2005 the
cumulative permanent reduction in fuel use is estimated at 4,613 million kg
of carbon dioxide (arising from reduced fuel use of 1,679 million litres);
Ø
the use of ‘no-till’ and ‘reduced-till’
farming systems. These production systems have increased significantly with
the adoption of GM HT crops because the GM HT technology has improved
growers ability to control competing weeds, reducing the need to rely on
soil cultivation and seed-bed preparation as means to getting good levels of
weed control. As a result, tractor fuel use for tillage is reduced, soil
quality is enhanced and levels of soil erosion cut. In turn more carbon
remains in the soil and this leads to lower GHG emissions. Based on savings
arising from the rapid adoption of no till/reduced tillage farming systems
in North and South America, an extra 2,929 million kg, of soil carbon is
estimated to have been sequestered in 2005 (equivalent to 8,053 million
tonnes of carbon dioxide that has not been released into the global
atmosphere). Cumulatively the amount of carbon sequestered may be higher
due to year-on-year benefits to soil quality. However, with only an
estimated 15%-25% of the crop area in continuous no-till systems it is
currently not possible to estimate cumulative soil sequestration gains.
Placing these carbon sequestration benefits within the
context of the carbon emissions from cars, Table 8, shows that:
Ø
In 2005, the permanent carbon dioxide savings from reduced
fuel use were the equivalent of removing nearly 0.43 million cars from the
road;
Ø
Cumulatively since 1996, the permanent carbon dioxide savings
from reduced fuel consumption since the introduction of GM crops are equal
to removing 2.05 million cars from the road for one year (8.5% of all
registered cars in the UK);
Ø
The additional probable soil carbon sequestration gains in
2005 were equivalent to removing nearly 3.6 million cars from the roads;
Ø
It is not possible to estimate the probable soil carbon
sequestration gains since 1996 (see above);
Ø
In total, the combined GM crop-related carbon dioxide emission
savings from reduced fuel use and additional soil carbon sequestration in
2005 were equal to the removal from the roads of nearly 4 million cars,
equivalent to about 17% of all registered cars in the UK.
Table
8: Context of carbon
sequestration impact 2005: car equivalents
|
Crop/trait/country |
Permanent carbon dioxide savings arising
from reduced fuel use (million kg of carbon dioxide) |
Average family car equivalents removed
from the road for a year from the permanent fuel savings |
Potential additional soil carbon
sequestration savings (million kg of carbon dioxide) |
Average family car equivalents removed
from the road for a year from the potential additional soil carbon
sequestration |
|
US: GM HT soybeans |
176 |
78,222 |
2,195 |
975,556 |
|
Argentina: GM HT
soybeans |
546 |
242,667 |
4,340 |
1,928,889 |
|
Other countries: GM
HT soybeans |
55 |
24,444 |
435 |
193,333 |
|
Canada: GM HT canola |
117 |
52,000 |
1,083 |
481,520 |
|
Global GM IR cotton |
68 |
30,222 |
0 |
0 |
|
Total
|
962 |
427,556 |
8,053 |
3,579,298 |
Notes: Assumption: an
average family car produces 150 grams of carbon dioxide of km. A car does
an average of 15,000 km/year and therefore produces 2,250 kg of carbon
dioxide/year
Concluding comments
GM technology has, to date delivered several specific
agronomic traits that have overcome a number of production constraints for
many farmers. This has resulted in improved productivity and profitability
for the 8.5 million adopting farmers who have applied the technology to over
87 million hectares in 2005.
During the last ten years, this technology has made
important positive socio-economic and environmental contributions. These
have arisen even though only a limited range of GM agronomic traits have so
far been commercialised, in a small range of crops.
The GM technology has delivered economic and
environmental gains through a combination of their inherent technical
advances and the role of the technology in the facilitation and evolution of
more cost effective and environmentally friendly farming practices. More
specifically:
Ø
the gains from the GM IR traits have mostly been delivered
directly from the technology (yield improvements, reduced production risk
and decreased the use of insecticides). Thus farmers (mostly in developing
countries) have been able to both improve their productivity and economic
returns whilst also practicing more environmentally friendly farming
methods;
Ø
the gains from GM HT traits have come from a combination of
direct benefits (mostly cost reductions to the farmer) and the facilitation
of changes in farming systems. Thus, GM HT technology (especially in
soybeans) has played an important role in enabling farmers to capitalise on
the availability of a low cost, broad-spectrum herbicide (glyphosate) and in
turn, facilitated the move away from conventional to low/no tillage
production systems in both North and South America. This change in
production system has made additional positive economic contributions to
farmers (and the wider economy) and delivered important environmental
benefits, notably reduced levels of GHG emissions (from reduced tractor fuel
use and additional soil carbon sequestration).
The impact of GM HT traits has, however contributed to
increased reliance on a limited range of herbicides and this poses questions
about the possible future increased development of weed resistance to these
herbicides. Some degree of reduced effectiveness of glyphosate (and
glufosinate) against certain weeds may take place. To the extent to which
this may occur, this will increase the necessity to include low dose rates
applications of other herbicides in weed control programmes (commonly used
in conventional production systems) and hence may marginally reduce the
level of net environmental and economic gains derived from the current use
of the GM technology.
No-till farming means that the ground is not ploughed at all, while
reduced tillage means that the ground is disturbed less than it would be
with traditional tillage systems. For example, under a no-till farming
system, soybean seeds are planted through the organic material that is
left over from a previous crop such as corn, cotton or wheat
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