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Although
bacterial diseases are relatively few, they can cause dire economic losses. For
example, bacterial soft rots of fruits and vegetables cause an estimated 50 to
100 million dollars in losses per year worldwide (Perombelon and Kelman 1980).
Efforts to eradicate Citrus canker caused by Xanthomonas campestris pv. citri
from the Gulf States resulted in the destruction of over 20 million trees in
nurseries or groves (http://www.floridaenvironment.com/programs/fe00124.htm
and
related links), and the problem has not been resolved. It should be noted that
antibiotics are not used to control most bacterial diseases of plants,
including Citrus canker.
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Bacterial diseases of plants are very difficult
to manage. In addition to visible disease symptoms, bacteria can become systemic
in a plant’s vascular tissue making it impractical to eradicate the pathogen
by pruning out symptomatic tissues or by applying a pesticide to the plant
surface. Moreover, bacteria undergo exponential growth, meaning that their
populations can double several times daily, depending on the bacterial species
and environmental conditions. Thus, bacterial diseases are explosive; by the
time symptoms are recognized, the pathogen often is entrenched and well on its
way to destroying the crop.
Managing bacterial diseases depends mostly on
host resistance (which may not be available in desirable crop varieties),
sanitation (e.g., preventing the introduction of pathogens and removing
diseased plants), and cultural practices (e.g., avoiding overhead
irrigation and limiting nitrogen fertilization). In some cases, chemical
bactericides (e.g., copper compounds and antibiotics) and biological
control agents are effectively integrated into the disease management program.
This article focuses on the role of antibiotics in plant disease control, with
emphasis on fire blight of apple and pear, the target of greater than 90% of the
use of antibiotics on crop plants (http://usda.mannlib.cornell.edu/reports/nassr/other/pcu-bb/).
Just the facts: Who, what, where,
why, how, and
to what extent?
What are antibiotics and which antibiotics are
used on plants? The classic definition
of an antibiotic is a compound produced by a microorganism that inhibits the
growth of another microorganism. Over the years, this definition has been
expanded to include synthetic and semi-synthetic products. Antibiotics are
grouped based on chemical structure or the mechanism of inhibition of
microorganisms. Table 2 illustrates the major classes of antibiotics and their
uses in crop protection, animal agriculture, and human medicine. Of the myriad
antibiotics used in agriculture, only two compounds are used on crop plants in
the U.S.: streptomycin and oxytetracycline.
Streptomycin. In
the U.S., streptomycin use is permitted on 12 plant species, but the primary
uses are on apple, pear, and related ornamental trees for the control of fire
blight caused by Erwinia amylovora (Table 3). Minor uses include
floriculture, seed treatment, and on seedlings of celery, pepper, potato,
tomato, and tobacco in the greenhouse and/or field. At high concentrations,
streptomycin can be phytotoxic to plants; thus it is applied to the surface of
plants and not injected.
Oxytetracycline.
This antibiotic is used primarily on peach, nectarine, and pear (Table
3).
Oxytetracycline also is used on an emergency basis on apple in specific regions
where streptomycin-resistant strains of E. amylovora have been
documented. Tetracycline derivatives are the only antibiotics that also can be
used internally in plants. Tetracyclines are injected into the trunks of palm
and elm trees to treat lethal yellows diseases caused by phytoplasmas (Agrios
1997). The injection of tetracycline into a tree is a labor-intensive and
expensive treatment, which often must be repeated for abatement or delay of
symptoms. Antibiotic injections are practical only for isolated high-value
ornamental trees and not vast plantings of agricultural or forest trees.
What quantities of antibiotics are used on
plants? In 1997, approximately 30,800
pounds of streptomycin and 26,700 pounds of oxytetracycline were applied to
fruit trees in the major tree-fruit producing states (Tables 3,
4, 5; NASS 1997).
This accounts for about 0.1% of total annual antibiotic use in the U.S.
Referring to pounds of antibiotics produced or used is a bit overwhelming and
incomprehensible. For example, the Centers for Disease Control and Prevention (CDC)
estimates that 50 million pounds of antibiotics are produced annually in the
U.S. (http://www.cdc.gov/ncidod/dbmd/
antibioticresistance/Default.htm)
and translates this into 230 million doses of antibiotics consumed by humans.
The following figures may help depict antibiotic use on plants. Nationwide in
1997, antibiotics were applied once or twice to 25% of apple acreage, four or
five times to about 40% of pear acreage, and four times to 8% of peach and
nectarine acreage (Table 3; NASS 1997). Not included in these figures is the
sale of streptomycin in small quantities to home gardeners. This probably
represents a tiny fraction of total sales but would be a significant source of
exposure to antibiotics if the purchaser were careless in handling the product.
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In commercial orchards, antibiotic powders are mixed in a large volume of water
to a concentration of 50-200 parts per million (ppm) and blown into tree
canopies with a high-pressure (air-blast) sprayer pulled by a tractor |
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Regulation of antibiotic use
on plants
| Facts
on Antibiotic Use on Plants in the U.S.
Two
antibiotics (streptomycin and oxytetracycline) are used on plants.
Use
on plants accounts for about 0.1% of total antibiotic use.
Antibiotic
use on plants is regulated by the Environmental Protection Agency.
Antibiotics
are applied to about 25% of apple acreage; 35-40% of pear acreage; and
8% of peach and nectarine acreage.
Controlling
fire blight of apple, pear, and related ornamental plants accounts for
the majority of antibiotic use on plants. |
Like all pesticides, antibiotic use on
crops and ornamental plants is regulated in the U.S. by the Environmental
Protection Agency (EPA). The registration process involves evaluation of the
toxicity and carcinogenicity of a product or its derivatives and also impacts
that a chemical may have on non-target species including plants, pollinating
insects, aquatic organisms, and other wildlife. Regulatory decisions are not
based on the efficacy of disease control. In comparison to most pesticides,
streptomycin and oxytetracycline are relatively non-toxic and have been assigned
the lowest toxicity rating of the EPA, category IV (EPA R.E.D. fact sheets:
http://www.epa.gov/REDs/). |
The use of pesticides on certified organic
crops is regulated by state or regional certification programs, and national
standards are under development. In certified organic farming systems, the use
of antibiotics is strictly limited to pear and apple for the control of the
bacterial disease fire blight (http://www.ams.usda.gov/nop
for national program, http://www.wa.gov/agr/fsah/organic/BNML00-PestDisease.htm for Washington state
standards, and http://www.ccof.org/section8.htm
for California standards).
According to the Organic Materials Review Institute, streptomycin and
oxytetracycline are included in the national list of permitted materials as
regulated materials. "Regulated materials" are those that can be used
if no alternatives are feasible and efforts to reduce use of such materials are
included in the farm plan. Antibiotics are not permitted on any other crops in
certified organic fields.
Product labels [http://fruit.wsu.edu/labels/fungicide.htm]
and supplemental literature state what type of clothing, gloves, and respirators
must be worn by mixers, applicators, and persons entering an area shortly after
antibiotics have been applied. Re-entry into the sprayed area without protective
gear is forbidden for 12 hours after using streptomycin or oxytetracycline. It
is a violation of federal law to use any pesticide, including antibiotics, in a
manner inconsistent with its labeling.
Product labels also specify a preharvest
interval (PHI), the period of time between the last permitted application and
harvest. PHIs are established to ensure that pesticide residues do not exceed a
predetermined limit or "tolerance." The PHIs for oxytetracyline and
streptomycin range from 21 to 60 days, depending on the crop and antibiotic.
Residue tolerances of 0.25 ppm and 0.35 ppm of streptomycin and oxytetracycline,
respectively, on produce have been established by the EPA based on toxicology
tests.
Fire blight: The primary target
for antibiotic
use on plants
In 1998, apple and pear growers in Washington
and northern Oregon suffered an estimated 68 million dollars in losses due to
outbreaks of fire blight caused by E. amylovora (http://www.goodfruit.com/archive/Apr15-99/special1.html).
Since 1997, approximately 500,000 pear trees have been destroyed in the Po
Valley of Italy, which is the major pear production area of the world, in an
effort to eradicate fire blight (Calzolari et al. 1999 and
http://www.goodfruit.com/archive/Apr15-99/special1.html). Another 580,000
pear, apple, and quince trees were destroyed in Romania between 1993 to 1997 and
340,000 pear and apple trees were destroyed in Croatia since 1995 in efforts to
halt the spread of fire blight in those countries (Cvjetkovic et al. 1999,
Severin et al. 1999).
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An apple or pear orchard may see little fire
blight for several years and then succumb to an epidemic when environmental
conditions favorable to the disease coincide with bloom (van der Zwet and Beer
1991). Fire blight is broken down into several subcategories such as blossom
blight, shoot blight and rootstock blight, each named for the tissue that is
infected and killed. Additionally, "trauma blight" can occur on
shoots and fruits due to wounds from hailstorms or wind. Blossom blight is the
phase best controlled by antibiotics (van der Zwet and Beer 1991). In the U.S.,
blossom blight is most common in the western states on pear, whereas shoot and
rootstock blight have caused devastating losses in apple orchards throughout the
U.S. and Europe.
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In order to understand fire blight control
strategies, a basic understanding of the disease is needed. The pathogen, E.
amylovora, overwinters in cankers or infected tissues from the previous
season. In the spring, as
temperatures increase, the pathogen multiplies in the cankers and spreads to
open blossoms. When temperatures exceed 15° C (60° F), the pathogen multiplies
rapidly on the stigmas of blossoms. After the population size of the pathogen
exceeds about one million cells per blossom, infection occurs. After infection,
the pathogen grows internally in the plant causing cell death, which is seen as
wilting and blackening of the infected tissues. Once these symptoms are visible,
there is no effective chemical treatment for fire blight. To minimize further
disease spread, the grower must prune branches at least 12 inches below the
visible symptoms. Depending on where infection occurs on a tree, the result can
be the loss of major fruit-bearing limbs or the entire tree.
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Fire blight management is multifaceted, with
antibiotics being just one component (Johnson and Stockwell 1998, van der Zwet
and Beer 1991). Sanitation, the removal of diseased tissues, is the most
important practice for fire blight control. Pre-bloom copper sprays also can
decrease populations of the pathogens at canker margins, but copper generally is not
used after bloom due to phytotoxicity that results in blemished fruit. While all
commercial pear varieties are susceptible to the disease, genetic resistance
exists in apple cultivars such as Red Delicious and Winesap. However, consumer
demand determines which apple varieties are produced and many newer popular
varieties, such as Gala, Fuji, Braeburn, Honeycrisp, and Pink Lady, are highly
susceptible to fire blight (van der Zwet and Beer 1991). Furthermore, many
semi-dwarfing apple rootstocks, which have desirable horticultural
characteristics, are very sensitive to fire blight. Infections of blossoms or
shoots can spread internally to the rootstock and kill the tree rapidly (van der
Zwet and Beer 1991).
Antibiotics are effective during the growth phase
of the pathogen on the surface of flowers before infection. Streptomycin
has been the antibiotic of choice as it kills the pathogen (bactericidal).
Oxytetracycline, which stops the growth of pathogen but does not kill existing
populations (bacteristatic), is less effective than streptomycin (McManus and
Jones 1994). The length of time that an antibiotic is active on the surface of
the flower is not well understood, but generally streptomycin is considered
active for 3 days and oxytetracycline for 1 day after application. Timing is
critical to the use of either antibiotic for fire blight control: unnecessary
sprays are expensive, but an omitted spray during an infection period can set
the stage for an epidemic.
EPA-approved product labels recommend spraying
antibiotics for fire blight control on a calendar basis, beginning during bloom
and repeating every 3 to 5 days until a specified time before harvest (http://fruit.wsu.edu/labels/fungicide.htm).
With that schedule, up to 15 streptomycin sprays and 10 oxytetracycline sprays
could be applied. If every acre of pear were sprayed at the maximum dose, then
264,810 pounds of streptomycin and 88,270 pounds of oxytetracycline would be
applied annually. Spraying every acre of apple at the maximum dose would result
in application of 802,455 pounds of streptomycin and 400,221 pounds of
oxytetracycline every year. Comparing these figures to those shown in Table 3
makes it clear that growers are actually using less than 5% of the amount of
antibiotic permitted.
Most growers are prudent in their use of
antibiotics because (i) antibiotics are very expensive (about $25 to $30 per
acre for the product and an additional $20 application expense); (ii) growers
wish to minimize selection pressure for antibiotic resistant strains of the
pathogen (see below); and (iii) research has demonstrated that there is little
or no benefit to spraying later than the bloom period. Growers rely on
recommendations of university-based Extension personnel and disease-risk models
to optimize the timing of antibiotic sprays and to minimize the number of
applications. Disease-risk models for fire blight evaluate weather factors to
predict if conditions are favorable for the disease and if antibiotics should be
sprayed (e.g. COUGARBLIGHT http://www.ncw.wsu.edu/fbsmith.htm for a description
and http://www.ncw.wsu.edu/FB2000f.htm for the model; MARYBLYT
http://www.intrepid.net/afrs/fb8.htm;
for a comparison of several models see: http://www.ipm.ucdavis.edu/DISEASE/DATABASE/fireblight.html).
While none of the models are perfect in predicting when and where fire blight
will occur, they are useful management tools that have spared growers and the
environment many antibiotic sprays.
Data from individual states illustrates shifts
in antibiotic use on apple and pear in the 1990s (Tables 4 and
5). Growers in
most major apple-producing states sprayed streptomycin an average of two times
per year, but the percentage of acreage that was treated varied greatly among
states (Table 4). Although alternating sprays of
streptomycin and oxytetracycline might alleviate the selection for resistance to
either or both antibiotics, the practice of EPA has been to grant special
registration of oxytetracycline on apple only after
streptomycin resistance in E. amylovora has been confirmed. Thus
oxytetracycline is used on apple only on a limited basis in
areas where streptomycin-resistant strains of E. amylovora have been
documented. An increase of apple acreage treated with antibiotics during the
1990s may reflect the increased planting of popular apple varieties that are
highly susceptible to fire blight.
A greater percentage of pear acreage was
sprayed with antibiotics during the 1990s compared with apple acreage (Table
5).
This is probably because of the greater inherent susceptibility of pear to fire
blight compared to apple and the tendency of pear to remain in bloom for
prolonged periods, especially in California.
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Secondary blossoms or flowers that open after fruit are developing, are common in
California orchards and are particularly vulnerable to fire blight, thus
requiring additional antibiotic sprays. After Extension educators publicized the
prevalence of streptomycin-resistant strains of E. amylovora in
Washington (Loper et al. 1991), streptomycin was rarely used on pear in that
state. Many pear growers have adopted oxytetracycline, or
combinations of oxytetracycline and streptomycin for fire blight control.
Biological control arrived on the fire blight
control scene relatively recently. A naturally occurring, non-pathogenic
bacterium, Pseudomonas fluorescens strain A506 (BlightBan A506, Plant
Health Technologies, Fresno, CA) was used on 30% of the pear acreage in
California in 1997 and 18% of the apple acreage in Washington in 1997 (NASS
1997). The
biocontrol bacterium competes with the pathogen for nutrients and space on the
stigmas of flowers. The competition from the biocontrol bacterium keeps the
pathogen from reaching large population sizes, decreasing the number of
infected blossoms by about half. Biocontrol can be integrated into antibiotic
spray programs (Stockwell et al. 1996a). The combination of the biocontrol and
streptomycin provides greater control than either implemented alone (Lindow et
al. 1996). Unlike antibiotics, which lose effectiveness over a few days,
biocontrol bacteria multiply and persist on blossoms. It is too early to
determine the impact of biological control on management practices of fire
blight. However, at least in theory, using biological control bacteria will
reduce selection for antibiotic-resistant strains of E. amylovora by
reducing pathogen populations and the number of antibiotic sprays needed.
Antibiotic resistance:
The silver bullet is
tarnished
Although the amount of antibiotics used on
plants is meager compared to medical and veterinary uses, streptomycin-resistant
plant pathogens have emerged (Table 6), which further complicates control of
bacterial diseases of plants. Surveillance for antibiotic-resistant plant
pathogens has been sporadic and usually in response to a disease control failure
in the field. Many, if not most, surveys for streptomycin-resistant E.
amylovora have come up negative; Table 6 reports only positive results.
Surveys have not detected oxytetracycline resistance in E. amylovora (Loper
et al 1991; Palmer and Jones 1999) but have identified tetracycline resistance
genes in nonpathogenic bacteria in apple orchards (Palmer and Jones 1999).
In E. amylovora, two genetically
distinct types of streptomycin resistance have been described (Table
7; Chiou
and Jones 1995a,b): (i) a point mutation in the chromosomal gene rpsL
which prevents streptomycin from binding to its ribosomal target; and (ii)
inactivation of streptomycin by a phosphotransferase, encoded by strA and
strB. The chromosomal mechanism occurs naturally in populations of E.
amylovora at a rate of about 1 in 10 billion cells. The genes strA
and strB are usually carried on pieces of DNA that can move among
bacteria. The level of resistance (minimal inhibitory concentration) conferred
to bacteria is greater from a chromosomal mutation, which renders the cell
insensitive to the antibiotic, than from the production of a phosphotransferase
enzyme that inactivates streptomycin (Shaw et al 1993). It should be noted,
however, that the level of resistance conferred by the enzyme is still about
five times greater than the concentration at which streptomycin is used in the
field.
Streptomycin resistance in most isolates of E.
amylovora has been attributed to chromosomal mutation because the majority
of resistant isolates obtained from different locations do not harbor strA-strB.
However, a quantitative survey to determine the relative prevalence of the
resistance mechanisms in various geographical regions has not been undertaken.
Molecular studies show that the chromosomal mechanism of resistance has arisen
independently in E. amylovora multiple times (Chiou and Jones 1995b;
McManus and Jones 1995).
The genes strA and strB usually
reside on transposons carried on plasmids, mobile pieces of DNA that are
generally not required for basic bacterial functions but that frequently carry
antibiotic resistance genes. Transposon Tn5393 carries strA and strB
in streptomycin-resistant strains of Erwinia, Pseudomonas, and Xanthomonas
on plants (Chiou and Jones 1993; Sundin and Bender 1996a,b). StrA and strB
have been identified in at least 17 environmental and clinical bacteria
populating diverse niches (Sundin and Bender 1996a,b), and in most cases, the genes
are on plasmids. In bacteria associated with animals, the plasmids carrying
genes for streptomycin resistance are usually small (<10 kb) and able to
exist in a broad range of bacterial species. These small plasmids do not have
the genes necessary to move from cell to cell. However, they can be transferred
with help from other bacterial gene products. In contrast, the resistance
plasmids in plant-associated bacteria are usually large (>30 kb), relatively
specific for certain bacterial host species, and able to accomplish their own
cell-to-cell transfer. In fact, the most common resistance plasmid in E.
amylovora is identical to a resistance plasmid found in P. agglomerans
(formerly called Erwinia herbicola), a nonpathogenic bacterial species
that is commonly found in apple orchards on trees, grasses, and weeds. This has
led to the hypothesis that E. amylovora acquired the resistance genes strA
and strB from its nonpathogenic cohorts (Chiou and Jones 1993). This could occur through plasmid transfer between two
different bacteria living in close proximity on plant surfaces. An exception to
the rule of relatively large resistance plasmids in plant-associated bacteria is
the discovery of a small plasmid, similar to the broad host range plasmid
RSF1010, in a few isolates of E. amylovora (Palmer et al 1997).
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Hypothesized acquisition of
streptomycin resistance genes (strA-strB) by Erwinia
amylovora.
Click on image for enlargement and more
information. |
Regardless of the mechanisms, streptomycin
resistance appears to be a stable trait in plant pathogenic bacteria. A survey
of celery beds in Florida in the early 1990s detected widespread resistance to
streptomycin among isolates of Pseudomonas cichorii, the causal agent of
bacterial blight, even though streptomycin had not been used commercially for
disease control since the late 1960s (Pohronezny et al 1994).
Streptomycin-resistant isolates of E. amylovora still were detected in an
orchard in California 10 years after applications of the antibiotic were halted
(Moller et al 1980). Similarly, streptomycin-resistant strains of E.
amylovora remain widespread in Washington state (Stockwell et al,
unpublished data) even though usage of the antibiotic decreased dramatically in
the 1990s after it was reported that 88% of the surveyed orchards harbored
resistant strains (Loper et al 1991). Perhaps "compensatory
mutations," a phenomenon recently described in streptomycin-resistant Escherichia
coli (Levin et al 2000) accounts for the stability of streptomycin-resistant
plant pathogen populations in the absence of selection. In this scenario,
chromosomal mutations for antibiotic resistance may initially inflict a fitness
burden to the bacterium. However, as the bacterium evolves in the absence of
selection, it undergoes mutations that ameliorate the fitness costs. The end
result of compensatory mutations is that the streptomycin-resistant strains
persist.
Political Fallout
Does antibiotic use on plants pose a risk to
human health? This question is
the subject of contentious debate in the U.S., Europe, and elsewhere. One
consumer advocacy group in the U.S. has gone so far as to call for a ban on
antibiotics used as pesticides (Lieberman and Wootan 1998; Center for Science in
the Public Interest http://www.cspinet.org/reports/abiotic.htm). Growers,
however, defend their practice as being so limited in scope as to be
inconsequential to the emergence of antibiotic resistance in hospitals and
communities. With almost no research data to uphold either view, arguments are
frequently based on circumstantial evidence and fueled by passion.
The greatest concern of those opposed to
antibiotic use on plants is that spraying antibiotics in the open environment
and over physically large expanses of land might increase the frequency of
antibiotic resistance genes—not just streptomycin- and tetracycline-resistance
genes but any other resistance genes that might be carried on the same plasmid—thereby
increasing the risk of these genes finding their way into medically important
bacteria. This would require the transfer of resistance genes from plant- and
soil-borne bacteria to bacteria that reside on or in humans. The transfer would
have to occur somewhere between the orchard and the human gut, in an environment
sufficiently favorable to both the gene donor and the recipient. To date there
is no circumstantial or experimental evidence for such a scenario. In addition
to transfer of resistance genes from environmental bacteria to "human"
bacteria, the genes would have to be functional in their new bacterial host in
order to wreck havoc. We are aware of only one study in which this issue was
addressed. Palmer and Jones (1999) found that streptomycin and tetracycline
resistance genes were often carried on the same large plasmid in orchard
bacteria, but when the plasmid was put into E. coli, the new host was
resistant only to tetracycline and not to streptomycin or 10 other antibiotics.
Recently a Mexican company attempted to
register a plant-grade gentamicin formulation with the U.S. EPA, primarily for
fire blight control. The product is currently used on a variety of crops in
Mexico and Central America and suppresses fire blight in field tests. Gentamicin,
however, is a critical tool in human medicine, used alone or in combination with
other drugs for treatment of various infections. In its evaluation of the
product, EPA called on experts from CDC. The result of the consultation was that
all antibiotic use on plants was called into question. In October 1999,
the application for registration of gentamicin on crop plants in the United
States was withdrawn.
At this point, streptomycin and oxytetracycline
have been used on crop plants for the past 45 years and 25 years, respectively,
without reports of adverse effects on humans. The efficacy of these silver
bullets for control of plant diseases has been diminished in some areas due to
the emergence of antibiotic resistant strains of pathogens, but they remain
important tools for the management of some of the most serious plant diseases.
The existing registrations of streptomycin and oxytetracycline with the EPA
appear to be intact; however, it is extremely unlikely that any additional
antibiotics will become available for use on plants.
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