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An ASABE Meeting Presentation
Paper Number: 131574361
Sugarcane Harvesting System: a Critical Overview
Shaochun Ma, Manoj Karkee, Qin Zhang
Washington State University Center for Precision & Automated Agricultural Systems, Prosser, WA
99350, USA
Written for presentation at the
2013 ASABE Annual International Meeting
Sponsored by ASABE
Kansas City, Missouri
July 21 – 24, 2013
Abstract. In this paper, a critical literature review of sugarcane harvesting systems in the context of sugar and
biofuel production is conducted. For sugar production, sugarcane field burning is carried out worldwide before
harvesting to get rid of leaves and tops which would impede the harvest operation. However, field burning has
environmental consequences. Hence, the improvement in harvester performance will have an effect on costeffectiveness and sustainability of sugarcane production and also on the success of biofuel production.
Sugarcane is one of the most efficient biofuel feedstocks in commercial use. Harvest cost comprises a major
component of overall sugarcane production cost. We surveyed the merits and limitations of chopped billet and
whole stalk harvesting systems. Whole stalk harvesting can reduce juice loss and sugar deterioration while
chopped billet harvesting has higher efficiencies in handling high-tonnage and bent stalks. Moreover, new
technologies and innovations applied on cane harvesters for improving harvesting efficiencies and qualities are
investigated.
Finally, major issues requiring further research are identified and corresponding
recommendations are made for future studies. Analyzing the current issues and challenges, the main outcome
of this review is the identification of potential solutions that can be investigated to improve sugarcane
harvesting efficiency. Effective and efficient harvesting can make sugarcane production more viable, profitable
and sustainable, especially for biofuel use since it requires collecting both of stalks and trash.
Keywords. biofuel feedstocks; sugarcane harvesting; environmental consequences; cost-effectiveness;
sustainability
Introduction
Sugarcane originates from tropical South Pacific and the planting techniques were transferred to China, North
Africa, Spain, and America in 7th and 8th century (Fischer et al., 2008). According to World Crop and Livestock
Statistics published by the Food and Agriculture Organization (FAO) since 1950, world sugarcane growing area
The authors are solely responsible for the content of this meeting presentation. The presentation does not necessarily reflect the official
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[email protected] or 269-932-7004 (2950 Niles Road, St. Joseph, MI 49085-9659 USA).
increases from 6.3 million hectares to 25.4 million hectares (FAOSTAT, 2013). Before mechanical harvesting,
the sugarcane harvesting is labor-intensive which is done manually by various types of hand knives.
Sugarcane workers can easily get fatigued due to excessive stress on the joints and muscles (Clementson and
Hansen, 2008) and have safety issues because of harmful pests from plantations (Carvalho, 2012).
With the advent of sugarcane harvester, the productivity (acre/hr) is increased substantially and the costs are
reduced compared to manual harvesting. However, harvesting still remains to be one of the most costly
operations representing about 30% of total sugarcane production cost (Barker, 2007; Salassi, 2006; Salassi
and Barker, 2008). In some places, such as Hawaii, the field conditions become more challenging for
mechanical harvesting because of uneven terrain, rocky land and lodging problem. Harvesting cost will be
much higher in these places since considerable work is required to prepare the field and modify commercial
harvesters to be applicable to local field conditions. Furthermore, the production cost is a big barrier to the
commercialization of biofuel produced from sugarcane biomass feedstocks. Therefore, it is meaningful to
improve harvester performance and reduce harvesting operation cost which could help decrease the biofuel
production cost. .
The sugarcane chopper harvester and whole stalk harvester are two main technologies available today. The
chopper harvester introduced stalk chopping into pieces and saved one extra operation (i.e. uploading
windrowed stalks to wagon). However, chopped billets have more cutting area exposed to air leading to more
juice/sugar deterioration than whole stalk (Maleki and Jamshidi, 2011). The whole stalk harvesters are still
popular in areas with erect cane conditions because of low cane deterioration rate than cane billets (Lionnet,
1986). The disadvantage of whole stalk harvesting is that it cannot handle the lodging and bent canes (Spargo
and Baxter, 1975).
Biofuels, such as sugarcane ethanol, has 78% less Greenhouse Gas (GHG) emission than petroleum gasoline
and the GHG emission will be reduced additional 9% with the elimination of cane field burning (Wang et al.,
2008). Pre- and post-harvest burning is one of major contributors to sugarcane ethanol related GHG emission
and it is going to be phased out in future due to people’s global warming concerns. . In addition to releasing
CO2, sugarcane burning also results in acidic fine article emission, which has negative impact on air quality
and human health (Allen et al., 2004). The green cane harvesting, which is harvest sugarcane without openfield burning, presents environment benefits. However, its expansion in main sugarcane production region
depends on the improvements of harvesting technology because the machine needs to process more biomass
throughput than burnt cane. .
The issues and challenges with respect to high operation costs, juice/sugar deterioration, adaption to various
field condition and environmental consequences have been studied in the literature. It is necessary to
comprehensively review the relevant literature regarding these topics, so as to identify the merits and
limitations of current commercial sugarcane harvesting systems. This is the purpose of this review. In
addition, the review provides recommendations for future development based on the analysis of current stateof-the-art.
Sugarcane harvesting preparation
Pre-harvest burning is usually carried out before sugarcane harvesting which makes the process easier during
both manual and mechanical harvesting. Cane burning is conducted during the whole harvesting season and
most of trash, including tops and leaves, is burned off because of increased biomass throughput of green
harvesting and the more flexible operations (cutting, chopping, and conveying) (Rípoli, 2000). However, preharvest burning becomes one of the most sensitive environmental issues faced by local communities. In
recent years, governments are formulating relevant regulations, such as incentives, to help farmers switch from
burnt cane harvesting to green cane harvesting. Green cane harvesting has presented obvious environmental
benefits and it is the trend of cane harvesting process due to the less GHG emission. The transition from burnt
cane harvesting to green cane harvesting makes tops and leaves separated from stalks that forms a surface
trash blanket. The green cane trash blanketing (GCTB) not only increases soil nutrient content, but also it is
resulted in better moisture retention and weed control (Page et al., 1986; Robertson and Thorburn, 2007;
2013 ASABE Annual International Meeting Paper
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Wood, 1991). The adoption of green harvesting is determined by the improved machine performance of
harvesters. Moreover, adaptable agricultural technologies and appropriate field preparation are needed to
make sugarcane harvesting more efficiently and effectively.
Burnt cane harvesting
Farmers conduct sugarcane burning as a standard pre-harvest practice throughout the world because it leads
to reduced pest stress and reduced cost of tops and trash handling (Boeniger et al., 1991; Humbert, 1963; King
et al., 1953; Semenzato, 1995). In addition, cane burning can get rid of trash which leads to increased fiber
and non-sucrose dissolved substances affecting the concentration of sucrose during sugar extraction process
(Bernhardt et al., 2000; Lionnet, 1986). However, the cane burning has various negative impacts in the sugar
yield. One of shortcoming is that there is a risk of saccharose deterioration reducing the rate of sugar
extraction. Therefore the burnt cane has to be processed within 15 days to avoid the fermentation of
saccharose to ethanol (Semenzato, 1995). Micro-organisms play an important role in cane deterioration.
Cane burning facilitates the micro-organism infection with wax removal, cane splits, and juice leakage (Lionnet,
1986).
In recent years, public pressure against cane burning is increasing throughout the world because of growing
environmental consciousness. In 1991, Boeniger et al. performed a survey and personal air sampling to
characterize worker’s exposure to biogenic silicate fibers. The survey and sampling showed that the air
concentration of biogenic silica fibers around harvesting workers was 56,000 fibers/m3 during harvesting
season (Boeniger et al., 1991). As a result of public concerns, US National Institute for Occupational Safety
and Health (NIOSH) investigated the disease risks of sugarcane workers exposed to biogenic silica fibers. The
reason is that biogenic silica fibers are found in sugarcane leaves and it is known as a causative agent to
esophageal cancers (Newman, 1986). In Brazil, Gisela and et al. (2008) reported that Polycyclic Aromatic
Hydrocarbons (PAH) content and mutagenic activity of organic extracts increase extensively because of cane
burning, cutting, and transporting in San Paulo State during sugarcane harvesting season.
Green cane harvesting
Figure 1. Green cane harvesting by John Deere 3522 sugarcane harvester
Considering the environmental effect, green cane harvesting could represent a sustainable management option
for sugarcane harvesting. The residues left in field from green harvesting can control weeds, reduce soil water
loss, decrease soil erosion, and improve nutrient cycling, soil quality, and productivity (Braunbeck et al., 1999).
In 2008, Núñez and Spaans reported that the weed control and irrigation costs after green harvesting were
reduced by 35% and 10% respectively (Núñez and Spaans, 2008). The soil fertility can be enhanced by
increased soil C and N content by 0.47 and 0.07 Mg/ha/year under green cane harvesting management (Cerri
and Cerri, 2007; Galdos et al., 2009; Goldemberg et al., 2008). From the standpoint of biofuel production, the
residues can be collected as biomass feedstocks. At this point, the investigations will be necessary to study
the tolerable removal rates of biomass residue from agricultural land that compromises soil sustainable
management (Karkee et al., 2012). However, the expansion of green cane harvesting depends on the
sugarcane mechanical harvesting technology improvement. There are several challenges faced by mechanical
2013 ASABE Annual International Meeting Paper
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green cane harvesting: (1) increased extraneous materials (such as mud, debris); (2) decreased cane
throughput because of trashes; and (3) increased harvesting cost. Comparing green cane and burnt cane
harvesting, Eiland and Clayton (1983) evaluated the fuel consumption and machine performance of four
mechanical harvesting systems in Florida and found that the fuel consumption was increased by 12% and the
harvesting efficiency (recovery rate) was decreased by 17%. Merits and weaknesses of burnt and green cane
harvesting management systems are summarized in Table 3 below.
Table 1. Green cane vs. burnt cane harvesting systems
Management
System
Pros
Cons
(1)Reduced trash handling cost; and
(2)pest control
(1)Sugar
deterioration;
and
(2)
environmental consequences of air
emission
(Boeniger et al., 1991; Humbert, 1963;
King et al., 1953; Semenzato, 1995;
Bernhardt et al., 2000; Lionnet, 1986)
(Semenzato, 1995; Lionnet, 1986;
Boeniger et al., 1991; Brazil, Gisela
and et al. 2008)
(1)Water and soil conservation; and
(2)weed control; reduction of pollutant
emissions
(1)Harvesting efficiency affected; and
(2)harvesting cost increased
(Braunbeck et al., 1999; Núñez and
Spaans, 2008; Cerri and Cerri, 2007;
Galdos et al., 2009; Goldemberg et al.,
2008)
(Eiland and Clayton, 1983)
Burnt cane
harvesting
Green cane
harvesting
Sugarcane harvesting technologies
Sugarcane can be harvested manually and mechanically. Harvesting sugarcane manually is a very laborintensive activity and agricultural labors are becoming scarce. The advent of mechanical harvesting frees
harvesting labors from drudgery field operations. Harvesting sugarcane mechanically makes green harvesting
possible since almost all manual harvested cane fields are burned to reduce labor cost (Han et al., 2012). Not
only is mechanical harvesting more productive, it also reduces greenhouse gas emissions from pre-harvest
burning of spiky leaves and tops necessitated by manual harvesting (Braunbeck et al., 1999). In addition, the
adoption of new technologies, such as GIS, GPS and sensing technologies on sugarcane harvester makes the
machine more cost-efficient, productive, and adaptable to various field conditions (Goswami et al., 2012).
Harvesting modes
Based on the form of harvested stalk, sugarcane harvesting can be categorized into two categories: billet
harvesting and whole stalk harvesting systems. The development of sugarcane harvesting machines can date
back to late 19th century (Spargo and Baxter, 1975). During the early period in Australia, the harvester is
consisted of cutting device, elevating system and knives severing the tops (King, 1969). . The earlier harvester
models were developed to process whole stalks. Later, a different harvesting mode was invented and a
sugarcane chopper harvester was commercialized due to the limitations of soldier (whole stalk) harvester
harvesting lodging and bent sugarcanes. The new harvesting concept was applied to new harvesters which
chop stalks into billets after base cutting and topping. Currently, sugarcane chopper harvester has been the
predominant model in the world, but whole stalk harvesting method are still employed in places (e.g. Louisiana)
where canes are mostly standing upright (Salassi and Champagne, 1996).
Whole stalk harvesting
Compared to chopped cane harvesting, whole stalk harvesters cut canes at the base and whole stalks are
conveyed to the field ground then arranged into a windrow for subsequent loading. Normally, post-harvest
burning is carried out to get rid of the trash such as leaves and tops before windrowed stalks being transported
to processing plant or storage site for future use (Salassi and Champagne, 1996). With erect stalks and wet
growing weather (cane chopper harvester could result in higher and mud levels), soldier (whole stalk) harvester
has been successfully used in Louisiana (Salassi and Champagne, 1996). Louisiana whole stalk harvesting
2013 ASABE Annual International Meeting Paper
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system (whole stalk harvester) is the main type of technology from which other similar harvesting systems are
derived (Braunbeck et al., 1999).
In addition, post-harvest deterioration of sugarcane (sucrose, glucose, and fructose) has been investigated in
the past by previous studies. The state of the stalk, such as whole stalk and billets, influences the cane
deterioration rate during the cut-to-crush delay (Lionnet, 1986).
Whole stalk harvesting method has
advantages in reducing the sugar/juice deterioration rate because of limited cutting section area exposed to
atmosphere which decreases the chances of organisms entering the stalk. In 2003, Singh and Solomon
reported that whole stalk had lower deterioration in terms of percentage of sucrose in juice and juice pH value.
Seven days after harvesting, whole stalk canes had 5.3% less loss in cane weight compared to cane billets
(Singh and Solomon, 2003).
The limitation of this mode is that the conveying system cannot handle bent stalks of lodged sugarcane and
has difficulties in harvesting heavy tonnage cane (Salassi and Champagne, 1996; Spargo and Baxter, 1975).
For lodged canes, the stalks are bent and twisted into various shapes which are challenging to form compact
bundles for being loaded to a wagon (Spargo and Baxter, 1975). Under the condition of high tonnage canes
with lodging issues, the cane recovery rate for a soldier harvester will be substantially declined because of its
limitations to handle bent canes.
Billet harvesting
Figure 2. Harvested sugarcane stalks in billet forms
The advent of billet harvesting is because whole stalk harvester cannot handle the bent or lodged canes well.
After base cutting and topping, the stalks are chopped into billets which have a uniform size for easily handling.
Wagons run along with the harvester for loading chopped billets directly which saves one more working
procedure. Compared to billet harvesting, whole stalk harvesting needs other sugarcane equipment to pick up
the windrowed sugarcane stalks to wagons. In 1955, Ken Gaunt, an Australian engineer, proposed the
concept of chopping cane into pieces after base cutting due to the material handling problem of soldier
harvesters (DIISRTE, 2011). Gaunt led a team to fabricate the first sugarcane chopper harvester leading to a
basic technology (Spargo and Baxter, 1975). Later, other similar harvesting systems are derived from this
technology (Spargo and Baxter, 1975; Braunbeck et al., 1999). If sugarcane harvesting is defined to include all
relevant operations to collect stalks from the field, the sugarcane chopper harvester can be called “complete”
harvesters while the whole stalk harvesters can only be called “partial” harvesters (Burrows and Shlomowitz,
1992).
The disadvantage is that chopping process accelerates sugar deterioration and increases the sugar loss
because of the easy access of bacterial through abrasion, failure points and cutting end surfaces in chopped
2013 ASABE Annual International Meeting Paper
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billets. The harvested billets need to be milled as fast as possible. Studies conclude that the ideal sugar
quality can be maintained within 24 hours which makes the tighter schedule of cane shipment and processing
(Burrows and Shlomowitz, 1992). In addition, there also exists juice loss during cutting and chopping
operations because cane juice is squeezed out from the torn cells (Maleki and Jamshidi, 2011). Cane juice
loss leads to the reduced sugar yield and higher operation cost (Maleki and Jamshidi, 2011).
Harvesting scale
The capacity of sugarcane harvester is determined by the swath: (single-row or double-row) of cutting head.
Under the condition of same harvesting technology, double-row whole stalk harvesters have less operation
cost of single-row whole stalk harvesters (Salassi and Champagne, 1996). In 1996, Salassi and Champagne
compared the estimated performance rating for single-row whole stalk harvester, double-row whole stalk
harvester, single-row sugarcane chopper harvester, loader (combine harvester), transloader (whole stalk
harvester). Table 1. shows the operation costs for these three harvesters. Although the cost per hour for
single-row whole stalk harvester is 35% less than double-row whole stalk harvester, the cost per acre will be
69% less than double-row harvester because the capacity (acres/hr) is 61% less (Salassi and Champagne,
1996). For single-row sugarcane chopper harvester, the cost per hour is even higher than double-row whole
stalk harvester because of more working procedures and energy consumption. In past few decades, singlerow sugarcane chopper harvester had been widely used for sugarcane harvesting around the world since it is
more stable and efficient for high yield variety of sugarcane (Salassi and Champagne, 1998). In 2003,
Jakeway studied the application of cane and forage harvesters for biomass recovery. The average effective
productivity of cane harvester (two cane line) was 9.1 (recovered yield is 93.7 Mg/ha) Mg/hr, whereas forage
harvester (four cane lines) reached to 11.6 Mg/hr (recovered yield is 67.0 Mg/ha) (Jakeway, 2003). It turns out
that two-time swath does not make capacity double due to the different technology. Literature does not show
any operation cost estimation studies on double-row sugarcane chopper harvesters. In 2010, Deere &
Company introduced their first double-row harvester model (John Deere 3522) which increases the productivity
compared to the previous single-row models (John Deere 3510 and 3520) (Deere&Company, 2011). To
improve the harvesting capacity and reduce the operating costs, multi-row sugarcane harvesters are the trend
of harvesting technology development.
Table 2. Operation costs for three harvesting systems (25-35 tons/acre) (Salassi and Champagne, 1996)
Systems
1
2
3
Harvesters
Single-row whole
stalk
Double-row whole
stalk
Single-row
chopper
$/hr
Acres/hr
$/acre
53.97
1.67
32.32
82.69
4.33
19.1
86.59
1.87
46.3
New technologies
Automatic guidance
With the revolution of electronics in last several decades, the precision farming (PA) tools such as automatic
guidance technology has been successfully applied to agricultural machines. To follow desired trajectory
during field operation leads to increased operation field efficiency of agricultural vehicles. The automation of
machine guidance of agricultural machines can date back to 1920s (Reid et al., 2000). In 1950s and 1960s,
the ‘driverless tractor’ prototypes were successfully guided by detecting the signal from the buried leader cable.
Later in the mid of 1980s, machine vision guidance system with image sensors had been developed for
agricultural combine harvesters for row crops (Li et al., 2009). Another technology breakthrough in this area is
the application of global positioning systems (GPS). As the agricultural vehicles is driven in a field, auto-steer
gathers GPS signals and steers the vehicles. GPS system plays an important role in automatic guidance of
off-road vehicle. With the advent of high accuracy GPS, such as Carrier Phase Differential GPS (CDGPS), the
accuracy of agricultural equipment operating had been increased to centimeter level (O’Connor et al., 1996).
With GPS-aided auto guidance system installed on the machine, the farmers and operators could set up
guidance paths at home and run harvesting machines according to the same guidance line (Case, 2009). The
Case IH Austoft 8000 series harvester operators can control guidance using a portable monitor facilitating them
2013 ASABE Annual International Meeting Paper
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to concentrate on sugarcane cutting instead of steering (Case, 2009). The auto-guidance systems technology,
which had been developed in past decades, becomes mature and these commercial products are available on
the market in recent years.
This auto-guidance system has also been adapted to sugarcane harvesting successfully. In 2012, Baio
evaluated the field performance of sugarcane harvester auto-guidance system in terms of accuracy, biomass
loss, and field efficiency. Compared to manual steering systems, the field pass-to-pass accuracy has been
greatly increased (Baio, 2012). Since sugarcane is a perennial crop, the harvester needs to stay on the rows
and reduce the damage of ratoon. The utilization of auto guidance can help operators to avoid the damage
even harvesting on night (Erickson, 2006).
Yield monitor system
PA technology had been widely applied to various cropping systems around the world. However, it is
challenging to adopt PA in sugarcane production because there are few commercial yield monitors being used
(Cox, 2002; Erickson, 2006). To overcome the bottleneck, researchers developed and tested a variety of
prototype yield monitors to recognize variation of agricultural land potential productivity. Yield monitor system
installed on harvesters is able to conduct yield mapping which target the management of inputs (fertilizer,
water, and etc.) to the farm land (Erickson, 2006; Griffin, 2010; Jhoty and Autrey, 1999; Shearer et al., 1999).
The sugarcane yield monitors can be categorized into two types based on monitoring concepts: weighing pads
(direct measurement); and indirect yield estimation using chopper pressure, elevator power or optical sensors.
Weighing pads have been employed by many researchers to measure the sugarcane yield. Wendte et al.
(2001) developed a deflection plate sensor for sugarcane yield monitoring, which includes a deflection plate
mounted nearby the billet discharge area and a load cell connected to the plate. Pagnano and Magalhaes
(2001) installed the weight sensor in the upper section of cross elevator. A low-pass filter was employed to
eliminate high-frequency noise. Benjamin et al. (2002) designed a similar cane yield monitoring system in
Louisinana State University. In this design, the weighing plate was mounted on the floor of cross elevator. The
R-Square value for the yield prediction is 0.97. Cox (2002) presented a yield mapping system for sugarcane
chopper harvesters with a weigh pad sensor. The technology has been commercialized by Case IH. In 2003,
Hernandez et al. introduced a biomass flow sensor coupled with the harvester roller feeder for cane mass-flow
rate measurement (Hernandez et al., 2003).
Indirect yield measurement includes use of optical sensors or machine power related parameters. Price et al.
developed a fiber optic yield monitoring system with three optical sensors mounted in the elevator floor to
estimate the sugarcane yield (Price et al., 2011). The result shows R-square value of 0.98 between the sensor
readings and actual yield (Price et al., 2011; Price et al., 2007). In 1996, Cox et al. studied the relationship
between billet mass flow rate and harvester power consumption showing that mass flow rate is proportional to
process power. Various pressure and speed sensors were installed to measure power consumed in chopping
and conveying systems. The chopping and conveying power consumption shows a linear relationship with
billet mass flow rate and the R-squares are 0.96 and 0.95 separately (Cox et al., 1996).
Table 3. Sugarcane yield monitor systems
Approach/outcome
A deflection plate sensor mounted to billet
discharge area.
A weigh pad was amounted in the upper section
of cross elevator and a low-pass filter was used
to eliminate high-frequency noises.
The weigh pat was mounted on the floor of cross
elevator and the R-square for the yield prediction
is 0.966.
A new weigh pad sensor was designed to
minimize the error due to dynamic conditions, to
reduce the noise due to external acceleration,
and to maximize its natural frequency.
A biomass flow sensor coupled with the
harvester roller feeder using a displacement
transmitter for biomass input measurement.
2013 ASABE Annual International Meeting Paper
References
Wente et al., 2001
Pagnano and Magalhaes, 2001
Benjamin et al., 2002
Cox, 2002
Hernandez et al., 2003
Page 6 of 12
A fiber optic yield monitoring system was
mounted in the elevator floor to estimate cane
yield and the R-square value is 0.98.
Cane mass-flow rate was estimated by
measuring power consumed in chopping and
conveying systems. The R-squares are 0.96 and
0.95.
Price et al., 2007; Price et al., 2011
Cox et al., 1996
Recent mechanical harvesting directions
For traditional harvesting, the typical harvester tops the cane plants, cuts cane at the base of stalk, chops the
stalk into billets (segments), and then remaining leaves are stripped off from stalks by primary and secondary
extractors. However, harvesting cane with leafy trash (such as tops and leaves) will affect the quality and
quantity of sugar extraction negatively (Eggleston et al., 2009). From the perspective of biofuel production,
cane trash (tops and leaves) can also be used for cellulosic ethanol production since it is composed mainly of
cellulose, hemicellulose and lignin which are potential sources of lignocellulosic materials and fermentable
sugars (Kim and Day, 2011). The fibrous residues, such as tops and leaves, left in the field through normal
harvesting contribute to about 15.1 Mg/ha which is 37% of whole cane plant dry matter and about 42% of cane
plant dry matter above the ground (Deepchand, 1986).
To harvest sugarcane biomass for biofuel refining, the cane residues are also needed to be collected for
conversion into ethanol. In Louisiana, the cane residues left in the field are typically 6-24 Mg/ha (Viator et al.,
2007). White et al. (2012) conducted research on the effects of green-cane harvesting on biomass and energy
yields. The study reported that the sugarcane chopper harvester can increase dry biomass yield by up to 13
Mg/ha with slow extractor fan speed and fans turned off which is a good strategy to harvest biomass as much
as possible (White Jr et al., 2012). Also in major growing areas, sugarcane tops is one of the largest biomass
resources of bioethanol feedstocks since it has enough amounts of sugar monomers (six and five carbon
sugars) (Dibanet, 2012; Sindhu et al., 2012). For instance, Stewart and Kingston estimated that the sugarcane
residue production is 2.6 million tons in dry matter compared to 2.75 million tons sugar production in
Queensland, Australia (Stewart and Kingston, 1979). In Hawaii, the average residue left after harvest is 18.2
Mg/ha (Jakeway, 2003)., Therefore, sugarcane residues, such as tops and leaves, are potential resources for
energy fuel production and it is worthwhile to collect them for energy use. Based on biomass harvesting
strategy for biofuel production, the tendency of cane harvester development in future is to modify the current
topper and extractor mechanism for harvesting biomass as much as possible.
In addition, it is necessary to modify cropping system to facilitate harvesting operation. Sugarcane grown on
raised bed allows a mechanical harvester to cut stalk at or under the soil surface (Richard et al., 1991). Since
the lower stem has higher level of sugar, cutting cane at ground level can harvest the bottom sugar-rich
internodes and increases total sugar yield (McIlroy, 1963). Furthermore, the shape of raised-bed cane growing
rows suit the base cutter to cut stalks at lower height and reduce cane damage (Hurney et al., 2005). In
addition, the raised bed system controls machine traffic and avoid compaction of top soil (Govaerts et al.,
2007).
In Hawaii, test plantings and harvestings revealed that sugarcane mechanical harvesting requires rock-free
farmland because rocks may damage the knife blades (Lee Jakeway, Hawaiian Commercial & Sugar
Company, personal communication). Considerable effort has to be spent on preparing the field to remove
surface and topsoil rocks for mechanical harvesting. From the perspective of cane harvesters working in the
rocky field, the new machine cutting head needs to be equipped with rock detection and real-time control
system which has the capacity to identify and avoid huge rocks by lifting the cutting head. In addition, preharvest cane burning is carried out to make the operation easier and more efficient. Switching to green cane
harvesting, it requires higher productivity to handle more biomass under the same conditions.
Conclusion and recommendations
Harvesting is a crucial component of sugarcane production system. In this paper we conducted a literature
review on sugarcane harvesting technologies in the context of both sugar and biofuel production. Moreover,
2013 ASABE Annual International Meeting Paper
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we identified the characteristics that current whole stalk harvesters and chopper harvesters have and
recommended relevant characteristics desired by sugarcane/energy cane harvesting systems for biofuel
feedstock production.
From the perspective of modern cane harvesting technologies, the design of more reliable and efficient
harvesters goes beyond minimizing harvest cost and biomass loss and includes the consideration of
minimizing negative impacts on environment and human health. The environmental issues and public pressure
against cane burning must be considered in combination with machine performance improvement. The
elimination of burning practices before sugarcane harvest has been and will led to more sustainable harvesting
systems, green cane harvesting, which has lower impact on nearby communities and environment. Although
higher harvest cost is incurred by handling increased volume of materials, the biomass recovery rate has been
improved substantially and hence higher increased biofuel yield.
Cane harvester design characteristics and capabilities are dependent upon the purposes of use: sugar
production or biofuel production. For sugar production, the harvesters need to be able to effectively separate
leaves and tops from stalks to increase the purity of extracted juice and reduce transportation cost. For biofuel
production, the harvesters need to be able to harvest as much biomass as possible since all of stalks, leaves,
and tops can be used as feedstocks for bio-refineries. The review identified that there is a lack of literature on
sugarcane/energy cane harvesting technologies for biofuel feedstock production. In recent years, commercial
harvesters that were developed for harvesting sugarcane for sugar production were used to harvest
sugarcane/energy cane for research in biofuel production. In future, specialized harvesting technologies and
machines need to be developed for green cane harvesting to support commercialization of cellulosic ethanol
production in US using sugarcane/energy cane crops.
Acknowledgements
The research presented in this paper was partially supported by Biomass Research and Development Initiative
(USDA-NIFA-9008-003540) and Washington State University Center for Precision and Automated Agricultural
Systems. Any opinions, findings, and conclusions expressed in this paper are those of the authors, and do not
necessarily reflect the views of USDA-NIFA or Washington State University.
Reference
Allen, A., A. Cardoso, and G. Da Rocha. 2004. Influence of sugar cane burning on aerosol soluble ion composition in
Southeastern Brazil. Atmospheric Environment 38(30): 5025-5038.
Baio, F. H. R. 2012. Evaluation of an auto-guidance system operating on a sugar cane harvester. Precision Agriculture
13(1): 141-147.
Barker, F. G. 2007. An economic evaluation of sugarcane combine harvester costs and optimal harvest schedules for
Louisiana. MS thesis. Baton Rouge, La.: Louisiana State University, Department of Agricultural Economics and
Agribusiness.
Benjamin, C. E. 2002. Sugar cane yield monitoring system. MS thesis. Baton Rouge, Louisiana: Louisiana State University,
Department of Biological and Agricultural Engineering.
Bernhardt, H., V. Pillay, and A. Simpson. 2000. Impacts of green cane harvesting on sugar factory operation at Sezela. In
Proc. 74th annual Congress of The South African Sugar Technologists’ Associaton (SASTA), 369-372. Durban, South
Agrica: University of Natal.
Boeniger, M. F., J. Fernback, R. Hartle, M. Hawkins, and T. Sinks. 1991. Exposure assessment of smoke and biogenic
silica fibers during sugar cane harvesting in Hawaii. Applied Occupational and Environmental Hygiene 6(1): 59-66.
Braunbeck, O., A. Bauen, F. Rosillo-Calle, and L. Cortez. 1999. Prospects for green cane harvesting and cane residue use
in Brazil. Biomass and Bioenergy 17(6): 495-506.
Burrows, G., and R. Shlomowitz. 1992. The lag in the mechanization of the sugarcane harvest: some comparative
perspectives. Agricultural History 66(3): 61-75.
Carvalho, P. N. de. 2012. ELLA policy brief: from manual to mechanical harvesting: reducing environmental impacts and
increasing cogeneration potential. Lima, Peru: Evidence and Lessons from Latin America (ELLA).
Case. 2009. Harvest feature: new sugarcane harvester comes precision farming ready. Australian Sugarcane 13(2): 11-11.
Cerri, C., and C. Cerri. 2007. Seqüestro de carbono em solos na América Latina. B. Inf. SBCS 32: 40-44.
Chanet, J., D. Boffety, G. André, T. Humbert, P. Rameau, A. Amamra, G. De Sousa, E. Piron, K. Hou, and F. Vigier. 2005.
2013 ASABE Annual International Meeting Paper
Page 8 of 12
Wireless technologies for field data acquisition. 2005 EFITA/WCCA Joint Congress on IT in Agriculture. Vila Real,
Portugal: Europen Federation for Information Technology in Agriculture.
Clementson, C., and A. Hansen. 2008. Pilot study of manual sugarcane harvesting using biomechanical analysis. Journal
of agricultural safety and health 14(3):309-320.
Cox, G., H. Harris, R. Pax, and R. Dick. 1996. Monitoring cane yield by measuring mass flow rate through the harvester. In
Proc. 1996 Conference of the Australian Society of Sugar Cane Technologists. B.T. Egan, eds. Queensland, Australia:
Watson Ferguson and Company.
Cox, G. J. 2002. A yield mapping system for sugar cane chopper harvesters. PHD Diss. Toowoomba, Australia: University
of Southern Queensland, Faculty of Engineering and Surveying.
De Aragao Umbuzeiro, G., A. Franco, D. Magalhaes, F. J. V. de Castro, F. Kummrow, C. M. Rech, L. Rothschild Franco de
Carvalho, and P. de Castro Vasconcellos. 2008. A preliminary characterization of the mutagenicity of atmospheric
particulate matter collected during sugar cane harvesting using the Salmonella/microsome microsuspension assay.
Environmental and molecular mutagenesis 49(4): 249-255.
Deepchand, K. 1986. Characteristics, present use and potential of sugar cane tops and leaves. Agricultural wastes 15(2):
139-148.
Deere & Company. 2011. Chairman's Message: Performance Stages Strong Rebound; Company Sets Ambitious Course
for Future. Moline, Ill.: Deere & Company World Headquarters. Available at:
https://www.deere.com/en_US/docs/Corporate/investor_relations/pdf/financialdata/reports/2011/2010chairmansmessag
e.pdf. Accessed 24 October 2012.
Deurveilher, D., F. Chiroleu, M. Chanet, J. Chanet, and D. Boffety. 2012. ICT for traceability of sugarcane harvesting
operations in small farms. International Conference of Agricultural Engineering CIGR-AgEng2012. Valencia, Spain:
International Commision of Agricultural Engineering.
DIBANET. 2012. Review of Biomass Feedstocks and Guidelines of Best Practice. D.2.2 Document: 16 October 2012.
Available at:
http://www.dibanet.org/library/website_admin/uploads/d22_review_of_biomass_feedstocks_and_guidelines_of_best_pra
ctice_full_version.pdf. Accessed 10 January 2013.
DIISRTE, 2011. History of Aussie Innovation. Canberra, Australia: Department of Industry, Innovation, Science, Research
and Tertiary Education Website Archive. Available at: http://archive.innovation.gov.au/ministersarchive2011. Accessed
12 May 2013.
Eggleston, G., M. Grisham, and A. Antoine. 2009. Clarification properties of trash and stalk tissues from sugar cane.
Journal of agricultural and food chemistry 58(1): 366-373.
Eiland, B., and J. Clayton. 1983. Unburned and burned sugarcane harvesting in Florida. Trans. ASAE 26(5): 1332-1336.
Erickson, B. 2006. Precision agriculture in Colombian sugar cane. Site Specific Management Center Newsletter:
September 2006. West Lafayette,Ind.: Purdue University. Available at:
http://www.agriculture.purdue.edu/ssmc/Frames/SSMCnewsletter9_2006.pdf. Accessed 17 December 2012.
FAOSTAT, 2013. Sugarcane Production in the World: 1950-2011. Food and Agriculture Organization of the United Nations
Statistical Database. Available at: http://faostat.fao.org/site/567/DesktopDefault.aspx?PageID=567#ancor. Accessed 9
May 2013.
Fischer, G., E. Teixeira, E. T. Hizsnyik, and H. V. Velthuizen. 2008. Chapter 2: Land use dynamics and sugarcane
production. In Sugarcane Ethanol: Contributions to Climate Change Mitigation and the Environment, 29-62. P. Zuurbier,
and J. V. D. Vooren, ed. Wageningen, the Netherlands: Wageningen Academic Publishers.
Galdos, M., C. Cerri, and C. Cerri. 2009. Soil carbon stocks under burned and unburned sugarcane in Brazil. Geoderma
153(3): 347-352.
Goldemberg, J., S. T. Coelho, and P. Guardabassi. 2008. The sustainability of ethanol production from sugarcane. Energy
Policy 36(6): 2086-2097.
Govaerts, B., K. Sayre, K. Lichter, L. Dendooven, and J. Deckers. 2007. Influence of permanent raised bed planting and
residue management on physical and chemical soil quality in rain fed maize/wheat systems. Plant and Soil 291(1-2): 3954.
Goswami, S. B., and M. S. Aruna, and S. G. Bairagi. 2012. A Review: The application of Remote Sensing, GIS and GPS in
Precision Agriculture. International journal of Advanced Technology & Engineering Research (IJATER): 2(1):50-54.
Griffin, T. 2010. Chapter 4: The spatial analysis of yield data. Geostatistical Applications for Precision Agriculture: 89-116.
Olive M. A., ed. New York, N.Y.: Springer-Verlag New York, LLC.
Han, J., J. B. Dunn, H. Cai, A. Elgowainy, and W. Q. Michael. 2012. Updated sugarcane parameters in GREET1_2012,
second revision. Chicago, Ill.: Argonne National Laboratory.
Hernandez, B., F. Fernandez, E. Ponce, L. Quintana, M. Esquivel, and J. Rodríguez. 2003. Sugarcane yield mapping from
2013 ASABE Annual International Meeting Paper
Page 9 of 12
the harvester biomass input flux. Programme book of the joint conference of ECPA-ECPLF. Werner, A. and A. Jarfe, ed.
Amstelveen, Netherland: Wageningen Academic Publishers.
Humbert, R. P. 1963. The Growing of Sugar Cane. 3rd ed. New York, N.Y.: Elsevier Publishing Co..
Hurney, A., B. Croft, D. Grace, and D. Richards. 2005. Final Report-SRDC Project BSS123: Influence of Harvester
Basecutters on Ratooning of Sugarcane. Available at: www.srdc.gov.au. Accessed 6 March 2013.
Jhoty, I., and J. Autrey. 1999. Precision agriculture-perspectives for the mauritian sugar industry. In Proc. 3rd Annual
Meeting of Agricultural Scientists, 15-21. Reduit, Mauritius: Food and Agricultural Research Council.
Karkee, M., R. P. McNaull, S. J. Birrell, and B. L. Steward. 2012. Estimation of Optimal Biomass Removal Rate Based on
Tolerable Soil Erosion for Single-Pass Crop Grain and Biomass Harvesting System. Transactions of the ASABE
55(1):107.
Kim, M., and D. F. Day. 2011. Composition of sugar cane, energy cane, and sweet sorghum suitable for ethanol production
at Louisiana sugar mills. Journal of industrial microbiology & biotechnology 38(7): 803-807.
King, N. J., R. Mungomery, and C. G. Hughes. 1953. 1st ed. Manual of cane-growing. New York, N.Y.: American Elsevier
Pub. Co.
KING, N. J. 1969. Historical review of sugarcane mechanisation in australia. In Proc. South African Sugar Technologists'
Association, 93-98. Durban, South Africa: South African Sugar Association.
Jakeway, L. A. 2003. Application of cane and forage harvesters for biomass fuel recovery. ASAE Publication No.
701P1103e. St. Joseph, Mich.: ASAE.
Li, M., K. Imou, K. Wakabayashi, and S. Yokoyama. 2009. Review of research on agricultural vehicle autonomous
guidance. International Journal of Agricultural and Biological Engineering 2(3):1-16.
Lionnet, G. 1986. Post-harvest deterioration of whole stalk sugarcane. In Proc. 60th Annual SASTA Congress, 52-57.
Durban, South Africa: South African Sugar Association.
Maleki, H. M.-G., and A. Jamshidi. 2011. Forecast model of sugar loss due to mechanical harvesting of the sugarcane crop.
Australian Journal of Basic and Applied Sciences 5(12): 1190-1194.
McIlroy, R. J. 1963. An introduction to tropical cash crops. 1st ed. Ibadan, Nigeria: Ibadan University Press.
Newman, R. 1986. Association of biogenic silica with disease. Nutrition and cancer 8(3): 217-221.
Núñez, O., and E. Spaans. 2008. Evaluation of green-cane harvesting and crop management with a trash-blanket. Sugar
Tech 10(1): 29-35.
Page, R., T. Glanville, and P. Truong. 1986. The significance of trash retention trials in the Isis and Maryborough mill
areas. In Proc. Conference of the Australian Society of Sugar Cane Technologists, 95-101. Brisbane, Australia: Watson
Ferguson & Co.
Pagnano, N., and P. Magalhaes. 2001. Sugarcane yield measurement. 3rd European Conference on Precision Agriculture.
Montpellier, France: ECPA.
Price, R., R. Johnson, R. Viator, J. Larsen, and A. Peters. 2011. Fiber Optic Yield Monitor for a Sugarcane Harvester.
Trans. ASABE 54(1): 31-39.
Price, R., J. Larsen, and A. Peters. 2007. Development of an optical yield monitor for sugar cane harvesting. ASABE Paper
No. 071049. St. Joseph, Mich.: ASABE.
Reid, J. F., Q. Zhang, N. Noguchi, and M. Dickson. 2000. Agricultural automatic guidance research in North America.
Computers and electronics in agriculture 25(1):155-167.
Richard, E. P., J. W. Dunckelman, and C. E. Carter. 1991. Productivity of sugarcane on narrow rows, as affected by
mechanical harvesting. Field Crops Research 26(3): 375-386.
Rípoli, T. C. C., W. F. Molina Jr, and M. L. C. Rípoli. 2000. Energy potential of sugar cane biomass in Brazil. Scientia
Agricola 57(4):677-681.
Robertson, F. A., and P. J. Thorburn. 2007. Management of sugarcane harvest residues: consequences for soil carbon and
nitrogen. Soil Research 45(1): 13-23.
Salassi, M. 2006. Survey Estimation of Sugarcane Chopper Harvester Costs in Louisiana. Journal American Society Sugar
Cane Technologists 26: 38-43.
Salassi, M. E., and F. G. Barker. 2008. Reducing harvest costs through coordinated sugarcane harvest and transport
operations in louisiana. Journal Association Sugar Cane Technologists 28: 32-41.
Salassi, M. E., and L. P. Champagne. 1996. Estimated Costs of Soldier and Combine Sugarcane Harvesting Stytems in
Louisiana. D.A.E. Research Report No. 703. Baton Rouge, La.: Louisiana State University Agricultural Center, Louisiana
Agricultural Experiment Station.
2013 ASABE Annual International Meeting Paper
Page 10 of 12
Salassi, M. E., and L. P. Champagne. 1998. A spreadsheet-based cost model for sugarcane harvesting systems.
Computers and electronics in agriculture 20(3): 215-227.
Semenzato, R. 1995. A simulation study of sugar cane harvesting. Agricultural Systems 47(4): 427-437.
Shearer, S., J. Fulton, S. McNeill, S. Higgins, and T. Mueller. 1999. Elements of precision agriculture: basics of yield
monitor installation and operation. PA-1. Lexington, Ky.: Kentucky Cooperative Extension Service, University of
Kentucky.
Sindhu, R., M. Kuttiraja, P. Binod, V. E. Preeti, S. V. Sandhya, S. Vani, R. K. Sukumaran, and A. Pandey. 2012. SurfactantAssisted Acid Pretreatment of Sugarcane Tops for Bioethanol Production. Applied biochemistry and biotechnology
167(6): 1513-1526.
Singh, I., and S. Solomon. 2003. Post-harvest quality loss of sugarcane genotypes under sub-tropical climate: Deterioration
of whole stalk and billets. Sugar Tech 5(4): 285-288.
Spargo, R., and S. Baxter. 1975. The development of the Australian chopped sugar cane harvester. Trans. ASAE 18(5):
806-810.
Stewart, G. A., and G. Kingston. 1979. Estimate of the production of sugarcane tops and trash in queensland. Resource
Recovery and Conservation 4(3): 239-246.
Viator, R., E. Richard, B. Viator, W. Jackson, H. Waguespack, and H. Birkett. 2007. Sugarcane chopper harvester extractor
fan and ground speed effects on yield and quality. Applied engineering in agriculture 23(1): 31.
Wang, M., M. Wu, H. Huo, and J. Liu. 2008. Life-cycle energy use and greenhouse gas emission implications of Brazilian
sugarcane ethanol simulated with the GREET model. International sugar journal 110(1317): 527.
Wendte, K. W., A. Skotnikov, and K. K. Thomas. 2001. Sugar cane yield monitor. U.S. Patents No. 6,272,819 B1.
White Jr, P. M., R. P. Viator, E. P. Richard Jr, and M. P. Grisham. 2012. Green-cane Harvest of Sugarcane Effects on
Biomass and Energy Yields and Nutrient Removal. In Proc. 2012 National Conference: Science for Biomass Feedstock
Production and Utilization. Knoxville, Tenn.: the Southeastern Regional Sun Grant Center.
Widden, M., and J. Blair. 1972. A new automatic tractor guidance system. Journal of Agricultural Engineering Research
17(1):10-21.
Wood, A. W. 1991. Management of crop residues following green harvesting of sugarcane in north Queensland. Soil and
Tillage Research 20(1):69-85.
2013 ASABE Annual International Meeting Paper
Page 11 of 12
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