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Part 2. APP and CHD Herbicides

 

 

Contents

 

2.1. Chemistry and Mode of Action

                 2.1.1. Inhibition of Fatty Acid Biosynthesis

                 2.1.2. Perturbation of the Trans-membrane Proton Gradient

2.2. Mechanisms Endowing Selectivity in Resistant Species

2.3. Evolution and Development of Resistance

2.4. Mechanism of Resistance in Weeds

2.5. Cross-resistance

 

 

 

2.1. Chemistry and Mode of Action

 

   APP (aryloxyphenoxy propanoate) and CHD (cyclohexanedione) herbicides are used to control grass weeds allover the world. These herbicides act as acetyl coenzyme A carboxylase (ACCase) inhibitors. Table 1 shows the ACCase inhibitors resistant weeds by species and country.

   The APP herbicides have been referred to by various group names in the literature. These include phenoxypropionates, arylpropanoates, and polycyclic alkanoic acids, but the APP is the most common name.

   Herbicides of APP group are usually formulated esters of the parent acid (e.g., diclofop-methyl, fenoxaprop-ethyl, fluazifop-butyl, etc.). Formulation as an ester facilitates penetration into leaf tissue. Shortly after entry into the leaf, the ester is hydrolyzed to release the parent acid. Thus, these herbicides form weak acid in plant tissue.

   The 3-hydroxy group in the CHD herbicides can deprotonate, conferring weak acid characteristics, but they are generally very labile and subject to rapid photolysis.

 

Table 1. The ACCase inhibitors most important two resistant weeds by species and country (WSSA 2004).

 

Herbicide resistance in weeds:

http://www.weedscience.org/Summary/UspeciesMOA.asp?lstMOAID=2

 

ACCase INHIBITORS (A/1) RESISTANT WEEDS
by species and country

#

Species

Country
(Click for Details)

Year

1.

Alopecurus myosuroides
Blackgrass

1982 - United Kingdom
1983 - Germany *Multiple - 2 MOA's
1993 - France
1996 - Belgium
1996 - Belgium *Multiple - 5 MOA's
1996 - The Netherlands *Multiple - 2 MOA's
1999 - The Netherlands
2001 - Turkey

1982

2.

Avena fatua
Wild Oat

1985 - Australia (Western Australia)
1986 - South Africa *Multiple - 2 MOA's
1988 - Australia (South Australia)
1990 - Canada (Manitoba)
1990 - Canada (Saskatchewan)
1990 - USA (Montana)
1990 - USA (Oregon)
1991 - Australia (New South Wales )
1991 - Canada (Alberta)
1991 - USA (Minnesota)
1991 - USA (North Dakota)
1991 - USA (Washington)
1992 - USA (Idaho)
1994 - Canada (Manitoba) *Multiple - 3 MOA's
1994 - United Kingdom *Multiple - 3 MOA's
1996 - Belgium
1996 - Canada (Saskatchewan) *Multiple - 3 MOA's
1996 - France
1997 - Canada (Manitoba) *Multiple - 4 MOA's
1997 - USA (Colorado)
1998 - Canada (Alberta) *Multiple - 3 MOA's
1998 - Chile

1985

3.

Avena sterilis
Wild Oat (sterilis)

1989 - Australia (New South Wales )
1989 - Australia (South Australia)
1993 - United Kingdom
1997 - Turkey
1998 - Turkey

1989

4.

Avena sterilis ludoviciana
Sterile oat

1992 - Italy
1996 - France

1992

5.

Brachiaria plantaginea
Alexandergrass

1997 - Brazil

1997

6.

Bromus diandrus
Great Brome

1999 - Australia (Victoria)

1999

7.

Cynosurus echinatus
HedgeHog DogTail

1999 - Chile

1999

8.

Digitaria ischaemum
Smooth Crabgrass

1996 - USA (New Jersey)

1996

9.

Digitaria sanguinalis
Large Crabgrass

1992 - USA (Wisconsin)
1993 - Australia (South Australia) *Multiple - 2 MOA's

1992

10.

Echinochloa colona
Junglerice

1994 - Costa Rica
1998 - Costa Rica *Multiple - 3 MOA's
2000 - Nicaragua

1994

11.

Echinochloa crus-galli
Barnyardgrass

2000 - USA (California) *Multiple - 2 MOA's
2001 - Thailand

2000

12.

Echinochloa oryzicola
Early Watergrass

2000 - USA (California) *Multiple - 2 MOA's

2000

13.

Echinochloa phyllopogon
Late Watergrass

1998 - USA (California)

1998

14.

Eleusine indica
Goosegrass

1990 - Malaysia
1997 - Malaysia *Multiple - 2 MOA's

1990

15.

Eriochloa punctata
Pasto Amargo

1997 - Bolivia

1997

16.

Hordeum glaucum
Wall Barley

2000 - Australia (South Australia)

2000

17.

Hordeum leporinum
Barley Grass

1996 - Australia (South Australia)
2001 - Australia

1996

18.

Ischaemum rugosum
Saramollagrass

2000 - Colombia

2000

19.

Lolium multiflorum
Italian Ryegrass

1987 - USA (Oregon)
1990 - United Kingdom
1990 - USA (North Carolina)
1990 - USA (South Carolina)
1991 - USA (Washington)
1992 - USA (Idaho)
1993 - France
1993 - USA (Virginia)
1995 - Italy *Multiple - 2 MOA's
1995 - USA (Georgia)
1998 - Chile
1998 - USA (Maryland)

1987

20.

Lolium perenne
Perennial Ryegrass

1995 - USA (Arkansas) *Multiple - 2 MOA's

1995

21.

Lolium persicum
Persian Darnell

1993 - USA (Montana)

1993

22.

Lolium rigidum
Rigid Ryegrass

1982 - Australia (South Australia) *Multiple - 7 MOA's
1982 - Australia (Western Australia) *Multiple - 3 MOA's
1984 - Australia (Victoria) *Multiple - 3 MOA's
1985 - Australia (New South Wales ) *Multiple - 3 MOA's
1992 - Saudi Arabia
1992 - Spain *Multiple - 2 MOA's
1992 - Spain
1993 - France
1993 - South Africa *Multiple - 2 MOA's
1996 - Tunisia
1997 - Chile
1997 - Greece
1998 - Israel

1982

23.

Phalaris minor
Little Seed Canary Grass

1993 - Israel
1996 - Mexico

1993

24.

Phalaris paradoxa
Hood Canarygrass

1996 - Mexico
1997 - Australia (New South Wales )
1998 - Italy

1996

25.

Rottboellia exalta
Itchgrass

1997 - USA (Louisiana)

1997

26.

Setaria faberi
Giant Foxtail

1991 - USA (Wisconsin)
1994 - USA (Iowa)

1991

27.

Setaria viridis
Green Foxtail

1991 - Canada (Manitoba)
1992 - Canada (Manitoba) *Multiple - 2 MOA's
1996 - Canada (Alberta)
1996 - Canada (Saskatchewan)
1996 - Canada (Saskatchewan) *Multiple - 2 MOA's

1991

28.

Snowdenia polystachea
Ethiopian grass

1998 - Ethiopia

1998

29.

Sorghum halepense
Johnsongrass

1991 - USA (Kentucky)
1991 - USA (Mississippi)
1995 - USA (Tennessee)
1995 - USA (Virginia)
1997 - USA (Louisiana)

1991

30.

Sorghum sudanese
Sudan Grass

1999 - Bolivia

1999

 

 

   Both APP and CHD herbicides are used for the selective control of grass weeds in cereal and dicot crops. Most of these two herbicidal groups are particularly active on annual grass weeds.

   The meristems (apical and intercalary) are the primary sensitive sites responsible for ultimate plant death in susceptible species (Shimabukuro, 1990). Growth of meristems is inhibited shortly after contact with diclofop-methyl and other APP and CHD herbicides, and chlorosis of emerged leaves is observed 3 to 4 days after herbicide application.

   Two mechanism of action have been proposed for APP and CHD herbicides: 1) a biochemical mechanism involving the inhibition of acetyl-CoA carboxylase (ACCase) and subsequent fatty acid biosynthesis in plastids, and 2) a biophysical mechanism involving the perturbation of the transmembrane proton gradient cross the plasma membrane (Powles and Holtum, 1994).

 

  2.1.1. Inhibition of Fatty Acid Biosynthesis

 

   Biosynthesis of fatty acids and lipids is essential to the normal growth and development of plants. Lipids are involved in the biogenesis and function of various membranes, cellular signal transduction and other physiological functions (Browse and Somerville, 1991). Fatty acid biosynthesis is localized in the chloroplasts and plastids of non-green tissues. The synthesis of malonyl-CoA catalyzed by acetyl-coenzyme A carboxylase (ACCase) (the key enzyme that regulates this biosynthesis) is the first committed step in fatty acid biosynthesis. The antibiotic cerulenin inhibits the condensation of the initial products in this biosynthesis giving similar end results to APP and CHD herbicides.

   Inhibition experiments also indicated that APP and CHD herbicides might act at the same site on ACCase (Rendiana et al, 1990). Collectively, the enzyme inhibition data indicated that APP and CHD herbicides are potent inhibitors of ACCase from grass species, and that selectivity between grass and dicot species is due to the relative insensitivity of dicot ACCase to these herbicides.

 

  2.1.2. Perturbation of the Transmembrane Proton Gradient

 

   It is demonstrated that all plant cells establish and maintain a transmembrane proton gradient that is vital to their growth and development (Serrano, 1985). The proton gradient is established (inside negative and outside positive at the plasma membrane) by an electrogenic (energy required) proton pump (H+– ATPase) that is driven by the hydrolysis of ATP.

  The free acids diclofop and haloxyfop depolarize the membrane potential or dissipate the transmembrane proton gradient in parenchyma cells of wild oat and other plants (Wright and Shimabukuro, 1987), while resistant dicots such as mung bean and sunflower are insensitive to membrane depolarization by APP herbicides.

   Sethoxydim does not affect H+– ATPase activity, but inhibits the plasma membrane-bound transmembrane redox potential (Weber and Luttge, 1988), an alternative mechanism for the establishment of the transmembrane proton gradient.

 

2.2. Mechanisms Endowing Selectivity in Resistant Species

 

   It is found that two mechanisms confer selectivity on grass and dicot crops that are resistant to APP and CHD herbicides. ACCase from dicot species is much less sensitive to in vitro inhibition by these herbicides than is ACCase from grasses. Many dicots crops do exhibit a substantial capacity for APP detoxification (Shimabukuro, 1990) and might be insensitive to membrane depolarization.

   Selectivity in different grass species is based upon at least on other mechanism. Grass crops such as wheat rapidly metabolize some APP herbicides to inactive products (Shimabukuro et al, 1987). Since the ester forms of these herbicides are nonphytotoxic, the first step in the metabolism of APP herbicides in both R and S species is usually deesterification of the nonphytotoxic ester to the parent acid. There is evidence that this bioactivation reaction is catalyzed by a carboxylesrease.

   The metabolism pathway for diclofop-methyl in wheat and wild oat has been investigated. Following deesterification, possibly outside the plasma membrane, diclofop acid is subject to aryl hydroxylation. The hydroxylated product is usually found in only very small quantities, due to rapid glycosylation of the hydroxyl group (Jacobson and Shimabukuro, 1984). Thus, the parent acid is depleted and the aryl glycoside accumulates rapidly in resistant grasses. The same process can occur in susceptible grasses, such as wild oat; however, less of the aryl glycoside is formed, and more of the glucose ester of diclofop. The latter product can be hydrolyzed in the tissue to release the parent acid again thus prolonging the presence of the herbicidally active compound.

   In wheat, the plasma membrane and plastid target sites are both sensitive to the action of diclofop. Nevertheless, inhibition of lipid biosynthesis and membrane depolarization are overcome by the rapid metabolism and detoxification of diclofop in intact tissues (Shimabukuro, 1990). However, wheat is susceptible to haloxyfop, fluazifop, and some other APP herbicides because of its ability to rapidly detoxify these herbicides.

 

2.3. Evolution and Development of Resistance

 

   Since the introduction of APP and CHD herbicides about 20 years ago, they have gained widespread popularity for control of grass weeds in both cereal and dicot crops. The practice of growing wheat in a monoculture, as is common in many parts of the world, has led to continuous use of these herbicides to control common weeds mainly Avena and Lolium species.

   As the APP and CHD herbicides provide control of grass weed only, evolution of resistance to these herbicides is restricted to grasses. Several weed species in which resistance to APP and/or CHD has been documented and that includes A. fatua and A. sterilis ((Devine and Shimabukuro, 1994). In most instances, resistance has developed after repeated use of herbicides from either or both chemical groups over several years. However, the patterns of resistance and cross-resistance within a species are variable. For example, although most of the resistant A. fatua lines from Canada are resistant to both APP and CHD herbicides, the relative degree of resistance to different products can vary among lines. In some cases there is a high level of resistance to APP herbicides but no resistance to CHD herbicides (Heap et al, 1993). Although it is often difficult to determine herbicide use histories, it appears that selection fore more than 4 years is sufficient too give rise to resistant populations. However, in situations where the herbicides may be applied more than once a year, this period may be shortened.  Other agronomic practices, such as the use of tillage or other mechanical weed control measures, may delay the development of resistance (Matthews, 1994).

 

2.4. Mechanism of Resistance in Weeds

 

   APP and CHD herbicides must reach the sensitive meristematic sites in their toxic forms at sufficient concentrations to disrupt normal growth and development of sensitive cells. In addition, herbicidal injury must be maintained at a threshold level over a critical period, after which irreversible damage results and death of cells becomes inevitable. Three key factors that influence the above processes are herbicide absorption and translocation, herbicide metabolism and detoxification, and sensitivity of the target sites (Devine and Shimabukuro, 1994).

   As previously mentioned, ACCase is well characterized as the target site of these herbicides. ACCase from most grasses is sensitive to both groups of herbicides. The fact that resistance to APP and CHD herbicides is not correlated with reduced ACCase sensitivity in some weeds, or with any other processes, often associated with herbicide resistance (e.g., uptake, translocation, and metabolism), supports the idea of another mechanism of resistance.  The evidence to occurrence of metabolism to the parent acid of these herbicides in wild oat resistant populations was not found. The alteration in the target site (ACCaes) was sufficient to give cause to resistant population as determined by a few studies. Physiological evidence indicated that APP and CHD both are bound to the same region of the target enzyme (Rendina et al., 1989). Furthermore, alteration in the binding site on ACCase enzyme was described as the mechanism of resistance in UM1 wild oat in Australia. 

   An altered ACCase enzyme confers herbicide resistance in different wild oat populations. Many populations show a high level of target site resistance (insensitive ACCase) (Murray et al., 1996). In wild oat populations, the levels of resistance vary from 0- to 300-fold resistance to specific ACCase inhibitors (Heap et al., 1993). Prior research on ACCase inhibitors resistant wild oat generally indicated high levels of resistance, in some instances, (e.g., <100-fold resistance to sethoxydim for UM1) (Heap et al., 1993).

 

2.5. Cross-resistance

 

   Cross-resistance in grass weeds such as wild oat was observed in many patterns, and the mechanism endowing cross-resistance in that weed was recognized. It occurs when a change at the site of action of one herbicide also confers resistance to herbicides from a different class that inhibits the same site of action, as selection by APPs for APP-resistant ACCase that is also less sensitive to inhibition by CHD (Powles and Holtum, 1994).

   It was found that resistance in wild oat lines occurred primarily in area where APP and CHD herbicides were used repeatedly. Only a few of these have been characterized based on cross-resistance patterns (Heap et al., 1993). Cross-resistant populations of wild oat were discovered to herbicides in Group 1 (ACCase inhibitors), Group 2 (ALS inhibitors) and Group 8 herbicides, triallate and difenzoquat (Morrison et al., 1995). All populations that lasted as resistant to triallate were also resistant to difenzoquat. As previously mentioned, physiological evidence indicated that APP and CHD both are bound to the same region of the target enzyme (Rendina et al., 1989). 

   However, different cross-resistance patterns characterize ACCase inhibitor resistance in weed (Moss, 1990; Heap et al., 1993). The clear differentiation between some types indicates that binding of APP herbicides may be more sensitive to changes in the ACCase than binding of CHD herbicides. Although unproven, it may well be that some mutation or conformation changes in vicinity of the ACCase inhibitor binding, but not CHD herbicides (Bourgeois et al., 1997). The first known instance of wild oat population exhibiting cross-resistance to both APP and CHD herbicides the <150–fold resistance of UM1 to sethoxydim is much higher than reported for ACCase–resistant maize mutants (Parker et al., 1993).

   In Egypt, no literature are available on the determination of resistant grass weed  populations to APP and CHD herbicides despite some of them are the principle compounds used to control these weeds for many years.

 

 

Herbicide mode of action important site :

http://ipcm.wisc.edu/uw_weeds/extension/articles/herbmoa.htm

http://www.agcom.purdue.edu/AgCom/Pubs/WS/WS-23.html

 

 

Global distribution of weed resistant ACCase web site :

http://www.weedscience.org/ACCaseDist.GIF

 

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