Alabama
Turfgrass Research Foundation
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Bang For Your Buck by Eddie Martin
All of us have heard and used this old clich'e, but in these times of ever-shrinking budgets it is a fact that has to be taken into consideration. When I was but a young lad, there were only two organizations to belong to: the Southern Turfgrass Association and the Golf Course Superintendents Association of America. Now we have a multitude of groups and organizations vying for our dollars. All of us have our own opinions about how much each one of these actually do for us personally. They all claim to be making great headway into promoting sod producers, golf course superintendents, lawn care specialists, and turf in general. I am not knocking any of these. There are some beneficial organizations out there, and each one of us must decide which ones to support. I can tell you that the turf industry in Alabama is privileged to have an organization that can help us on a personal level. It is an organization which allows the individual to have a direct input into what is being done with his or her membership dollars. The Alabama Turfgrass Research Foundation was established in 1997 by a group of individuals that saw this and had the foresight to act on it. With the commitment made by the charter members, and with the help of the Alabama Turfgrass Association and the Alabama Golf Course Superintendents Association, the ATRF has been able to do some exciting research. Air movement on putting greens, Virginia Buttonweed Research Project, Lovegrass Management in Zoysiagrass Sod Production, Sulfonyl Urea Herbicides for Southern Turf, Centipedegrass Liming and Fertilizer Issues and Water Use and Irrigation Scheduling for Bentgrass Putting Greens are just a few examples of research and studies supported by the ATRF. If the ATRF is to continue supporting research projects, we need your support. We ask that when you decide where your turfgrass dollars are going to be spent this year, please earmark a place in your budget for ATRF membership. It is a foundation that allows you to see your donations working for you. If you would like more information on the ATRF, if you have any suggestions on research, or if you would like to become a member, please contact one of the ATRF board members listed in the box at the right.
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ATRF Board of Directors President: Past President: Vice President: Education Rep: Board Members: Wayne Bassett Jeremy McDuffie Executive Secretary: |
Project
title
Disease management strategies for controlling spring dead spot in a ‘Tifway’ bermudagrass fairway
Rational
Spring dead spot (SDS) is a serious root-rot disease of bermudagrass, and particularly when the grass is managed intensively in golf course settings. Spring dead spot occurs more frequently in the states within the northern tier of the bermudagrass transition zone. There are over 2,200 golf courses located throughout the southeastern United States (10); it is estimated that 70 to 75% of those golf courses are symptomatic for SDS (personal communication, Mr. Patrick O’Brien, USGA Green Section, Southeast Director). The cost of applying fungicides for control of SDS is estimated to be well in excess of $3,000,000 per year.
Weed management and the selection of a pre-emerge for spring application is affected by SDS-diseased fairways. Necrotic patches that result from SDS typically green up in the summer from lateral bermudagrass growth of adjacent, healthy turf. Dinitroanilines, routinely applied as a spring pre-emerge for weed control, are mitotic inhibitors that delay lateral growth of bermudagrass into necrotic patches. As a result, a more costly pre-emerge, Oxadiazon, which does not restrict rooting of bermudagrass stolons, must be applied for weed control.
Spring dead spot has been a problematic disease of bermudagrass for more than a half century. Turfgrass managers continue to develop strategies for controlling SDS in bermudagrass. Although progress has been made to identify the causal organism(s) and define a disease profile, controlling SDS continues to require additional research. The optimum temperatures for growth of Ophiosphaerella korrae, a causal organism of SDS, range between 77 and 86oF (5,2). Bermudagrass plants infected by O. korrae and exposed to cold temperatures under controlled environmental conditions have a greater degree of SDS symptom expression (2,8). To date, however, the affects of soil temperature and soil moisture on SDS have not been examined in replicated studies in the field.
Benefits of research to golf course superintendents
Disease management strategies for controlling spring dead spot (SDS) of bermudagrass will be enhanced based on results of this proposed research. The precise time of year the SDS fungus is actively infecting bermudagrass roots will be identified. The influence of soil temperature and soil moisture on occurrence of infection and disease expression of SDS in a Tifway bermudagrass fairway will be determined. These environmental factors may be used as a tool for predicting occurrence of infection of bermudagrass roots. This approach is a key component of disease management. The resultant information can be applied to a specific time within the growing season for initiating aggressive disease management control measures. Integrated with temporal data, cultural management practices will be identified that promote plant health.
Objectives
1.
Define environmental factors in a
‘Tifway’ bermudagrass fairway that promote infection of bermudagrass by Ophiosphaerella
korrae, a causal organism of spring dead spot.
2. Evaluate cultural management practices for reducing the severity of spring dead spot in bermudagrass.
Methods and materials
The study will be located at Old Waverly Golf Course (site of the 1999 U.S. Women’s Open), West Point, MS. The number 9 fairway of ‘Tifway’ 419 bermudagrass with a history of severe spring dead spot is the site of this proposed research. The bermudagrass is managed intensively. Spring green-up is typically 20 days earlier than other bermudagrasses in the area and dormancy is delayed in the fall due to high management inputs. Spring dead spot has been observed every spring on this fairway for over ten years. Each year new necrotic patches appear and recurring necrotic patches enlarge in diameter. Based on global positioning mapping of the fairway boundary, over two thirds of the fairway had severe symptoms of SDS. A SDS disease severity rating of 10 (scale = 1-10, where 10 is severe) was recorded in April of 2004. Samples were collected from the margins of necrotic patches. Roots were washed free of soil and thatch debris, surface disinfested and plated onto 1/4 strength potato dextrose agar to recover O. korrae. Confirmation of the SDS causal organism was obtained using polymerase chain reaction (PCR) protocol.
In July of 2004, a study was initiated in an 84' x 69' area within the diseased fairway. Seven treatments were initiated in individual 12' x 15' plots, replicated four times in a randomized complete block design. Based on soil (pH 6.9) and leaf tissue analyses and an excessive thatch layer, the following treatments were included:
1. Core aerification (3/4" x 4" hollow tine); 3 to 4 aerifications per growing season
2. Chelated manganese (5 lb/acre-growing season)
3. Verticutting; 3 to 4 verticuttings per growing season
4. Elemental sulfur (200 lb/acre-growing season)
5. Eagle (myclobutanil) fungicide application 30-d prior to dormancy
6. Core aerification plus top-dressing with sand/reed sedge peat; 3 to 4 aerifications and top-dressing per growing season
7. Untreated control
In September of 2004, a chelated manganese treatment was applied in 1 lb applications on a bi-monthly schedule and elemental sulfur was also applied as a treatment. Two core aerification treatments, one included top-dressing, and a verticutting treatment were initiated. A fungicide application of Eagle will be applied 30 days prior to dormancy (1st week of November) at a rate of 1.2 oz product per 1,000 square feet.
Soil temperature and soil moisture will be monitored using Spectrum’s Watchdog™ weather monitoring sensors and data loggers. Watermark soil moisture sensors and external soil temperature sensors were placed within the root zone/soil interface of the untreated control plots. These sensors are connected to Watchdog data loggers that record on a 120 min schedule. All sensors will remain in place and record data throughout the duration of the study.
Turfgrass samples (2" x 4") will be collected on a monthly basis beginning September 2004 and continue throughout the study. Characteristics to be determined and recorded from these turf samples will include depth of thatch layer, root health, shoot and root dry weights, and frequency of O. korrae isolation.
1. The
depth of the thatch layer will be determined by measuring the thatch/mat
zone.
2. Root
health will be determined using a visual rating that is based on a scale of
0-5 where 0 = no discoloration and 5 = greater than 76% root discoloration.
3. Shoot
and root dry weights will be determined by thoroughly washing and separating
shoots and roots, drying them at 149o F for 24 hours, then
recording sample weights.
4. Frequency
of O. korrae occurrence in bermudagrass roots will be determined by
first washing roots in tap water to remove debris.
Root surface disinfestation will be carried out on root segments (0.5
in) by washing the roots in a 0.6% sodium hypochlorite solution and
triple-rinsing in sterile distilled water.
Dried roots will be placed onto 1/4 strength potato dextrose agar
supplemented with streptomycin sulfate and chloramphenical antibiotics.
Frequency will be based on the number of O. korrae isolates
recovered from the total number of roots.
5. Confirmation
of O. korrae will be achieved through PCR techniques described by
Tisserat et al. (12). DNA
amplification of unknown isolates will be accomplished using specific O.
korrae primers, OKITS1 and OKITS2.
The first phase includes extracting DNA from the unknown isolates
using a Dneasy Plant Mini Kit for isolation of cellular fungal DNA.
PCR protocol of Tisserat et al. (12) will be followed. Confirmation will be achieved when OK-primers amplify a
454-bp fragment from DNA of O. korrae isolates.
Turfgrass quality (visual rating on a scale of 0 to 9 where 9 = best) will be recorded for all treatments in the fall (October) and spring (April). Disease ratings (visual rating on a scale of 0 to 10 where 10 = severe) will be recorded in April.
Expected results
This project will define the relationships between soil temperature and soil moisture and the frequency of O. korrae in bermudagrass roots maintained under fairway conditions over the course of a calendar year. The resultant data will identify the time of the year O. korrae is actively infecting bermudagrass roots, as well as what influence soil temperature and soil moisture have on fungal activity, plant resistance, and symptom expression.
Cultural management practices will be employed as treatments on the Tifway bermudagrass fairway to determine influences on plant health and effects on disease severity. It will be determined whether an aggressive core aerification program can promote the development of healthy bermudagrass plants and the overall relationship to infection by O. korrae. The benefits of top-dressing with a sand:reed sedge peat mix will be identified. Reed sedge peat has a neutral pH that promotes beneficial bacteria and actinomycetes. These beneficial microorganisms may have antagonistic affects on O. korrae, thereby reducing or inhibiting O. korrae activity. Reed sedge incorporated into the root zone may promote the development of a healthy root system, thereby reducing fungal infection and/or SDS symptom expression. Composts of this nature have been successful for controlling take-all root rot of St. Augustinegrass (personal communication, Dr. Phil Colbaugh, Plant Pathologist, Texas A&M Research Center, Dallas, TX). Take-all root rot is caused by the ectotrophic root-infecting fungus, Gaeumannomyces graminis var. graminis.
Applications of sulfur or manganese to bermudagrass plots will stimulate a more acidic soil solution over time. The effect of acidic soil conditions on SDS development will be determined. The efficacy of myclobutanil fungicide for controlling SDS will be determined. Fungicide applications have not been a reliable single-component disease management tool for controlling SDS as compared to other turfgrass diseases.
This project will define parameters that will lead to a better understanding of the implementation of successful disease management strategies for controlling SDS of bermudagrass.
A graduate student (master’s level) will have extensive research responsibilities in this proposed project. Mr. Hunter Perry will receive his Bachelor’s of Science degree Spring 2005 in Golf and Sports Turf Management from Mississippi State University. As part of the required co-op, Mr. Perry spent eight months of 2004 at Farm Links Golf Club, Sylacauga, AL. In addition, during the eight month co-op, Mr. Perry was selected to serve as one of two United State Golf Association Green Section Interns for the Southeast region. With his experience in turfgrass management, impressive academic standing, and his desire to solve problems associated with turfgrass management, Mr. Perry has the potential to become a highly motivated graduate student that can bring much success to this turfgrass pathology research program, as well as gain professional training in the area of turfgrass pathology.
Literature review
Spring dead spot (SDS) is a serious disease of
bermudagrass (Cynodon dactylon [L.] Pers.), particularly the hybrid
bermudagrasses (Cynodon dactylon x Cynodon transvaalensis
Burtt- Davy). Spring dead spot
has been researched for more than a half century, and there are still many
‘unknowns’ yet to be defined. To
date, three fungi from the same genus, Ophiosphaerella, have been
identified as causal organisms of SDS of bermudagrass.
In the spring of 2004, Ophiospaerella. korrae was isolated
from roots of a Tifway bermudagrass fairway displaying severe symptoms of
SDS in Mississippi. Polymerase
chain reaction (PCR) as described by Tisserat et al. (12) was used to
confirm the identification of O. korrae (unpublished).
Spring
dead spot symptoms first appear during spring green-up of bermudagrass.
This disease occurs in bermudagrasses in home lawns, sports fields,
putting greens, fairways, tees, and roughs.
Necrotic patches of dead grass ranging from a few inches to several
feet in diameter can be observed throughout a bermudagrass stand.
The patches remain void of healthy bermudagrass through early summer
until lateral growth of adjacent bermudagrass fills in the dead spots.
These dead spots recur on an annual basis, typically becoming larger
in diameter each successive year. The
stolons, crowns, and roots of infected bermudagrass plants appear black and
rotted.
It
was observed during early descriptions of SDS that the disease was more
severe in bermudagrass that experienced a period of dormancy (13,14).
Several research projects conducted under controlled environmental
conditions resulted in similar conclusions on the influence of soil
temperature on the bermudagrass-O. korrae interaction and the
severity of SDS symptoms. Endo,
et al. (4) initiated Koch’s postulates by inoculating ‘Tifgreen’
bermudagrass with isolates of O. namari (15) and incubating the
grasses at 55 or 75oF. Disease severity was greatest among Tifgreen plants exposed
to 55oF, indicating a cold temperature effect in the disease
cycle. Similarly, Crahay et al.
(2) demonstrated when ‘Tufcote’ bermudagrass was infected by O.
korrae, symptom expression was more severe at 59oF compared
to 77 or 86oF. McCarty
et al. (8) concluded from their research of SDS-infected bermudagrass
exposed to low temperatures that cold temperatures (23 to 27oF)
induced a higher degree of SDS symptom expression and reduced shoot
development. Nus and
Shashikumar (9) reported that bermudagrass plants infected by O.
herpotricha or O. korrae are more susceptible to cold damage.
Spring dead spot of bermudagrass has been associated
primarily with hybrid bermudagrasses that are intensively managed.
Several management practices, or lack thereof, are considered to be
contributing factors for predisposing bermudagrass to SDS.
Early control programs consisted of managing nitrogen levels for
healthy turf, reducing the thatch layer, preventing compaction, managing
water inputs, and applying fungicides in a preventive manner (1,6).
This disease management strategy remains in extensive use today. Disturbance of the root zone through cultural practices has
been shown to reduce disease severity (11).
Adjusting soil pH (promoting acidic conditions with compounds such as
sulfur and manganese) also reduces SDS severity of bermudagrass (3).
To date, fungicides with efficacy for controlling SDS have not been
an exclusively reliable tool in the SDS disease management program (6,7).
Future research should focus on the response of bermudagrass to infection by O. korrae under natural growing conditions in the field, and determination of how this interaction can be manipulated to reduce severity of SDS in bermudagrass.
Bibliography
Baird,
J. H., Martin, D. L., Taliaferro, C.M., Payton, M. E., and Tisserat, N. A.
1998. Bermudagrass
resistance to spring dead spot caused by Ophiosphaerella herpotricha.
Plant Dis. 82:771-774.
Crahay, J. N.,
Dernoeden, P. H., and O’Neill, N. R. 1988.
Growth and pathogenicity of Leptosphaeria korrae in bermudagrass. Plant Dis. 72:945-949.
Dernoeden, P. H.,
Crahay, J. N., and Davis, D. B. 1991.
Spring dead spot and bermudagrass quality as influenced by nitrogen
source and potassium. Crop Sci.
31:1674-1680.
Endo, R. M., Ohr, H.
D., Krausman, E. M. 1985.
Leptosphaeria korrae, a cause of the spring dead spot disease of
bermudagrass in California. Plant
Dis. 69:235-237.
Iriarte, F. B., Wetzel, H. C., III, Fry, J. D., Martin, D. L., and
Tisserat, N. A. Genetic diversity
and aggressiveness of Ophiosphaerella korrae, a cause of spring dead
spot of bermudagrass. Plant Dis.
(In press).
Kozelnicky, G. M.
1974. Updating 20 years of
research; spring dead spot on bermudagrass.
USGA Green Section Record. 12:12-15.
Lucas, L. T.
1980. Control of spring
dead spot of bermudagrass with fungicides in North Carolina.
Plant Dis. 64:868-870.
McCarty, L. B.,
DiPaola, J. M., and Lucas, L. T. 1991.
Regrowth of bermudagrass infected with spring dead spot following low
temperature exposure. Crop Sci. 31:182-184.
Nus, J. L. and
Shashikumar, K. 1993.
Fungi associated with spring dead spot reduces freezing resistance in
bermudagrass. Hort Sci.
28(4):306-307.
The Golf Magazine
Golf Course Guide. http://www.golfcourse.com.
Tisserat, N. A, and
Fry, J. D. 1997. Cultural practices to reduce spring dead spot (Ophiosphaerella
herpotricha) severity in Cynodon dactylon. Int. Turf. Res. Inst. 47:54-59.
Tisserat, N. A.,
Hulbert, S. H., and Sauer, K. M. 1994.
Selective amplification of rDNA internal transcribed spacer regions to
detect Ophiosphaerella korrae and O. herpotricha.
Phytopath. 84:478-482.
Wadsworth, D. F. and
Young, H. C., Jr. 1960.
Spring dead spot of bermudagrass.
Plant Dis. Reptr. 44(7):516-518.
Wadsworth, D. F.,
Houston, B. R., and Peterson, L. J. 1968.
Helminthosporium spiciferum, a pathogen associated with spring
dead spot of bermuda grass. Phytopath.
58:1658-1660.
Wetzel, H. C., III, Skinner, D. Z., and Tisserat, N. A. 1999. Geographic distribution and genetic diversity of three Ophiosphaerella species that cause spring dead spot of bermudagrass. Plant Dis. 83:1160-1166.