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Final Report for
Project 11620 (Task/Deliverable #5)
Protecting Water Quality Through the Use of Effective Water and Nutrient Management Practices for Strawberry Production
Submitted to
Florida Department of Agriculture and Consumer Services
June 18, 2007
Investigator: C. D. Stanley
University of Florida, IFAS Gulf Coast Research and Education Center 14625 CR 672 Wimauma, FL 33598 Ph: 813-633-4117 Fax: 813-634-0001 E-mail: [email protected]
Cooperator: Alicia Whidden, Multi-county extension agent Hillsborough Co. Extension Office (South-central) 5339 SR 579 Seffner, FL 33584
Final Report for
Project 11620 (Task/Deliverable #5)
Protecting Water Quality Through the Use of Effective Water and Nutrient
Management Practices for Strawberry Production
Submitted to
Florida Department of Agriculture and Consumer Services
June 12, 2007
Investigator: C. D. Stanley University of Florida, IFAS Gulf Coast Research and Education Center 14625 CR 672 Wimauma, FL 33598 Ph: 813-633-4117 Fax: 813-634-0001 E-mail: [email protected]
Cooperator: Alicia Whidden, Multi-county extension agent Hillsborough Co. Extension Office (South-central) 5339 SR 579 Seffner, FL 33584 Project Duration: 3 years Requested Annual Funding Level: $70,000/year
Introduction and Justification:
Florida’s growers produce the majority of the nation’s winter crop fresh strawberries. With over 7000 acres dedicated to strawberries, the Hillsborough County’s Plant City-Dover area has long been known as the “Winter Strawberry Capitol of the World”. The farm value from strawberries was $140 million in 2002-03, up from $38 million twenty years ago. During that time, strawberry acreage has increased 40 percent, up from 5000 acres. Strawberry producers are among the most unique agricultural producers in the state and most aggressive in adopting technological improvements.
They were one of first commodities to utilize plastic-mulched raised-bed culture in the 1960’s. This allowed for soil sterilization, eliminating weeds, nematodes, soil borne insects and disease. The black plastic raised soil temperature for winter production and inhibited future weed germination. It also kept the berries out of the sand and reduced evaporative moisture loss. Unfortunately, the plastic mulch also eliminated the possibility of augmenting fertility during the production cycle. Since Florida’s strawberry production is during the winter, growers needed to freeze protect on occasion with overhead irrigation. By its very nature, this procedure wet the beds and leached nutrients from the beds during freeze protection. Since there was no way to determine before hand the number of freezes to come during a berry deal, growers would tend to fertilize on the high side, so there would be adequate fertility for the berry crop during the entire season. The advent of microirrigation (drip) allowed growers to place a measured amount of water and fertility at the root zone to mirror the plants needs without over-fertilizing or moisture loss through evaporation. Drip irrigation has reduced the amount of water needed to produce a crop of strawberries by about half and has reduced the industry’s rate of fertility by a third. Over 95 percent of the strawberry industry has embraced this technology. However, because strawberries arrive as bare root transplants the plants must be established by overhead irrigation. Additionally, the growers still must utilize overhead irrigation for freeze protection as needed. This requires the growers to have both overhead and drip irrigation systems. To reduce groundwater pumped from the aquifer, over 45 percent of the state’s acreage collects surface tailwater from the fields and reuses it. The water conserved through these practices is well documented. As an industry, strawberries are using less water than they did twenty years ago, with forty percent more acreage. However, there is little information on the quality of the water in groundwater, in tailwater, or in surface water discharged from the farm during a storm event. Project Objectives: The use of best management practices (BMP) for production of horticultural crops in Florida are being identified for producers to use to meet total maximum daily loadings (TMDL) regulations to minimize nutrient loading quantities in groundwater and surface water bodies. In some cases, producers adhering to approved BMP’s may have “implied compliance” and considered exempt from liability if TMDL limits are exceeded. The overall objective of this project is to evaluate the effectiveness of water and nutrient management practices for strawberry production
Page 2
(concentrating on those contained in the Vegetable and Agronomic Crop BMPs manual) under a range of soil type and individual grower management levels. The ultimate goal of the project is assess the level of BMP use, demonstrate effectiveness, and encourage grower adoption of water and nutrient management practices that will reduce the potential for contamination to shallow groundwater, surface runoff and surface water bodies. Achievement of this objective includes efforts to: A) Develop and conduct a survey of strawberry growers to ascertain an industry-wide estimation of base-level fertilization and irrigation practices to gauge Best Management Practice adoption and to survey producers following Project completion to establish the degree of adoption and success BMP’s designed to reduce groundwater contamination risks B) Assess actual commercial crop production scenarios (including differences in soil type, management level, fertilization and irrigation practices) for nutrient load potential of nitrogen from subsurface leaching and surface runoff. This information would be valuable to ascertain the state of the industry with respect to management practices which are used to minimize potential for off-site movement of applied nutrients. C) Use educational programs with results of field data, to assist growers in adopting water and fertilizer management technologies that will reduce the amount of N leaching each year from typical crop production systems. Sample management practices in use for this portion of the project include conversion to drip irrigation, optimum fertilization rates including pre-plant and fertigation systems, improvement of plant establishment and freeze protection irrigation efficiency through re-design of in-place irrigation systems, use of tissue testing to better track actual crop-nutrient contents and thereby avoid over fertilization, etc. Methodology A) This objective will seek to assess on an industry-scale and within the
grower-cooperator group participating the project, the pre- and post-study status of water and nutrient management practices. In addition, an effort to determine the economic impact of implementing BMP changes will be accomplished as part of the education process.
B) Through extension and industry personnel, grower-cooperators will
enlisted to allow surface and subsurface water sampling on a regular
Page 3
basis (weekly) to ascertain the impact of present water and nutrient management practices on water quality. All grower-cooperator irrigation and fertilizer application information will be available in the process of evaluation. Groundwater sampling would involve the use of multi-level water samplers (allowing simultaneous sampling at multiple depths) to determine the amounts of soluble inorganic N in the shallow groundwater beneath grower/cooperator production fields and surface runoff sampling and for the same nutrient analyses to assess off-site discharge during rainfall and overhead irrigation events at each location. Surface water sampling will be accomplished using automated event sampling equipment and/or regularly scheduled surface samples of static water bodies. Analyses will be accomplished using a rapid flow analyzer (RFA) which employs a spectrophotometric method for determination of nitrate-N in water samples.
C) This objective will be accomplished through ongoing education programs
(newsletter articles, EDIS publications, educational workshops) making growers aware of information which will encourage the use of BMP's that reduce potential of movement of applied nutrients of-site.
Anticipated Benefits: The most effective way to achieve adoption of BMP’s is for growers to see them successfully in use by fellow growers. The benefits that would result from this study would be identification of effective BMP’s that minimize any detrimental impact of applied nutrients on surface water and groundwater resources resulting from strawberry production. The industry survey conducted at the beginning and end of this project would provide evidence of those core practices which should be included in a BMP manual which is responsible for addressing strawberry production. The overall benefit to the public would be water quality protection of this natural resource.
Page 4
2004-2005 Progress Report The first year of this study was initiated in August 2004, by identifying grower/cooperators who: 1) had production fields containing specific soil types 2) were willing to share specific cultural management information
3) would allow water quality samples to be collected from production fields on a weekly basis.
Twenty sampling sites (shown in Figures 1-11) were identified and cooperative agreements were arranged with grower/cooperators and monitoring equipment was installed. A weekly water sampling scheme for strawberry production was implemented in November 2004 and continued through March 2005. Once strawberry production ceased, sampling continued at those locations where a double crop (i.e. melons, peppers, etc) was planted to follow the strawberries. This sampling scheme continued into mid June. During the production season a survey (Table 1.) was developed to ascertain the production inputs and management practices of the grower cooperators. The results of the survey showed some variability in management practices, but nothing extremely divergent among sites. Generally, for a projected 120-day strawberry crop, producers were applying 0 to 30 lbs N as dry pre-plant fertilizer and 0.75-1.5 lbs N applied as liquid fertilizer per day. Irrigation applications ranged from 45 min/day to 3 hr/day depending on emitter flow rate and grower preference. However the majority of producers were applying irrigation water at 60 min/day. Fertilizer was injected at mid- to late-irrigation cycle with enough time left to flush the system before the irrigation cycle concluded. Specifically, the following general conclusions resulted from the responses to the survey: 1) growers use drip irrigation with overhead sprinklers for transplant
establishment and cold protection 2) crops are planted mid to late October 3) growers use at least five different microirrigation tube types amongst the
responses 4) growers use drip tube with 0.24 to 0.50 gpm/100 ft application rates 5) growers apply irrigation rates from 0.12 to 0.26 inches/A/day 6) ~ 50% of growers apply no dry pre-plant fertilizer 7) growers that do apply dry pre-plant fertilizer apply ~ 20 to 40 lb N per acre 8) growers apply ~ 1 lb N per acre per day liquid fertilizer 9) growers use experience to decide when and how much to irrigate (with a
limited number using soil moisture measurements) 10) growers fertigate at the end of the cycle with ~15 to 30 flush time.
Page 5
Soil types of the sites identified included Immokalee, Pomello, St. Johns, Seffner, Zolfo, Kesson, Ona, Taveres, Malabar, Lake, Gainesville, Candler, Fort Meade, and Myakka. All sites had dry season water table levels below 2 m, so a sampling modification of using a “wick”-type leachate collector (Figure 12) was implemented. This collector allowed for collection of water and nutrients leaching below the crop rooting zone and allowed an estimated of mass balance losses of N and water from the fields. An analysis of the results from the water quality sampling showed that most growers leached < 1lb N03-N for the season but losses of >20 lb N03-N for the season were measured (Figures 13-24). A comparison of N03-N losses to soil type showed no significant relationship reinforcing the probability that N03-N losses that do occur are more likely due management intensity. Overall, based on these first year results, the strawberry grower/cooperators participating in this study seem to be doing an exceptional job of minimizing water and nutrient losses during the production season. Information from this first year of data collection will be presented at the Florida Strawberry Growers Association Agritech 2005 meeting this August.
Page 6
Table 1. Grower/Co-operator Cultural Information Sheet Site #: ________ Cultivar: _______________ Planting Date(s):_________________________ Irrigation System(s): _____________________________________________ Drip Tube Type: ____________________________________________ Emitter Spacing: ____________________ Emitter Flow Rate: ______________ Daily Runtimes (minutes): Nov. _____________________ Dec.________________________ Jan. ______________________ Feb.________________________ Mar. _____________________ Apr.________________________ Dry Fertilizer Analysis: ______________________________________ Dry Fertilizer Application Rate: ________________________________ Liquid Fertilizer Analysis: _____________________________________ Liquid Fertilizer Application Rate: Nov. __________________ Feb. ______________________ Dec. __________________ Mar. ______________________ Jan. ___________________ Apr. _______________________ How do you determine irrigation runtime? At what point in an irrigation cycle do you inject fertilizer?
Page 7
!( !(
!(Site 3
Site 2Site 1ONA
MYAKKA
ZOLFO
MYAKKA
MYAKKA
POMELLO
ST. JOHNS
ARCHBOLD
ST. JOHNS
TAVARES
MYAKKA
WINDER
BASINGER
ARENTS
ARCHBOLD
ZOLFO
ONA
ONA
POMELLO
ST. JOHNS
IMMOKALEE
SMYRNA
MYAKKA
SEFFNER
WINDER
ARCHBOLD
ST. JOHNS
ARCHBOLD
SEFFNER
ONA
MALABAR
HAPLAQUENTS
POMELLO
ARCHBOLD
ARCHBOLD
POMELLO
ARENTS
ONA
SEFFNER
SEFFNER
SMYRNA
ST. JOHNS
MALABAR
ST. JOHNS
BASINGER
BASINGER
POMELLO
MYAKKA
POMELLO
ST. JOHNS
WINDER
POMELLO
SMYRNA
SEFFNER
MALABAR
POMELLO
SEFFNER
POMELLO
TAVARES
SMYRNA
WINDER
POMELLOSMYRNA
BASINGER
ZOLFO
ARCHBOLD
ZOLFO
ZOLFO
ARCHBOLD
ST. JOHNS
ST. JOHNSPOMELLO
IMMOKALEE
ONA
ST. JOHNS
BASINGER
ST. JOHNS
BASINGER
IMMOKALEE
SMYRNA
BASINGER
ZOLFO
IMMOKALEE
ARCHBOLD
MYAKKA
Figure 1
Page 8
!(!(
!(Site 6
Site 5
Site 4
SEFFNER
MYAKKA
FORT MEADE
ONA
WINDER
SEFFNER
MYAKKA
SEFFNER
ST. JOHNS
ST. JOHNS
ARENTS
SEFFNER
MALABAR
ST. JOHNS
FORT MEADE
ST. JOHNS
ARENTS
ST. JOHNSMYAKKA
SMYRNA
ZOLFO
MALABAR
MALABARMYAKKA
MALABAR
MYAKKASMYRNA
SMYRNA
MYAKKA
FORT MEADE
FORT MEADE
ST. JOHNS
MYAKKA
BASINGER
BASINGER
MYAKKA
SMYRNA
WINDER
Figure 2
Page 9
!(Site 7
LAKE
ZOLFO
FELDA
BASINGER
FORT MEADE
BASINGER
KESSON
MYAKKA
ST. JOHNS
BASINGER
MALABAR
GAINESVILLE
BASINGER
SEFFNER
LOCHLOOSA
MYAKKA MYAKKA
SEFFNER
PAISLEY
Figure 3
Page 10
!(
Site 8
BASINGER
ONA
ONA
BASINGER
ONA
SEFFNER
MYAKKA
LAKE
LAKE
MYAKKA
SEFFNER
SEFFNER
Figure 4
Page 11
!(Site 9
CANDLER
LAKE
IMMOKALEE
TAVARES
ST. JOHNS
TAVARES
ST. JOHNSMYAKKA
CANDLER
MYAKKA
IMMOKALEE
BASINGERMYAKKA
BASINGER
MALABAR
LAKE
MALABAR
SEFFNER
Figure 5
Page 12
Site 10
MYAKKA
MALABAR
ST. JOHNS
BASINGER
ST. JOHNS
BASINGER
ST. JOHNS
TAVARES
MALABAR
Figure 6
Page 13
Site 13Site 12
Site 11
LAKE
BASINGER
GAINESVILLE
SEFFNER
LAKE
SEFFNER
BASINGER
LAKE
LAKE
ST. JOHNS
BASINGER
BASINGER
BASINGER
KENDRICK
BASINGERBASINGER
Figure 7
Page 14
!(Site 14
SEFFNER
ONA
ZOLFO
ST. JOHNS
Figure 8
Page 15
!(
!(Site 16
Site 15
LAKE
ZOLFO
CANDLER
ZOLFO
LAKE
TAVARES
FORT MEADE
ZOLFO
BASINGER
FORT MEADE
BASINGERSEFFNER
SEFFNER
MYAKKA
KENDRICK
LAKE
MYAKKA
FORT MEADE
TAVARES
BASINGER
Figure 9
Page 16
Site 19Site 18
Site 17
ONA
ONA
ZOLFO
MYAKKA
SEFFNERFORT MEADE
ZOLFO
SEFFNER
ST. JOHNS
ZOLFO
BASINGER
SEFFNER
BASINGER
ST. JOHNSMYAKKA
ONA
ST. JOHNSST. JOHNS
ST. JOHNS
ST. JOHNS
ST. JOHNS
ZOLFO
ONA
SEFFNER
ST. JOHNS
ST. JOHNS
ST. AUGUSTINE
MYAKKA
MYAKKA
Figure 10
Page 17
Site 20MYAKKA
SEFFNER
ZOLFO
ONA
ONA
PAISLEY
ST. JOHNS
ONA
EATON
WINDER
ZOLFO
ONA
BASINGER
BASINGER
SMYRNA
BASINGER
Figure 11
Page 18
Site 21
Figure 12
Page 19
10"
6.5"
3.5"
Field soil
Perforated disc
Fiberglass rope
Sample collection chamber
Sample collection access tube
Figure 13
Page 20
0 50 100 150 200Days
0
5
10
15
20
Nitr
ate-
N p
er A
(lbs
)
Site 1Site 2Site 3
Farm 1Sites 1, 2, and 3
St. Johns
Immokolee
Pomello
Figure 13a
Page 21
0 50 100 150 200Days
0
0.05
0.1
0.15
0.2
Nitr
ate-
N p
er A
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)
Site 4Site 5Site 6
Farm 2Sites 4, 5, and 6
St. John’s
Seffner
Zolfo
Figure 14
Page 22
0 50 100 150 200Days
0
0.05
0.1
0.15
0.2
0.25
Thou
sand
ths
Nitr
ate-
N p
er A
(lbs
)
Site 7
Farm 3Site 7
Kesson
Figure 15
Page 23
0 50 100 150 200Days
0
0.005
0.01
0.015
0.02
0.025
0.03
Nitr
ate-
N p
er A
(lbs
)
Site 8
Farm 4Site 8
Ona
Figure 16
Page 24
0 50 100 150 200Days
0
0.005
0.01
0.015
0.02
0.025
0.03
0.035
Nitr
ate-
N p
er A
(lbs
)
Site 9
Farm 5Site 9
Taveres
Figure 17
Page 25
0 50 100 150 200Days
0
0.5
1
1.5
2
2.5
Nitr
ate-
N p
er A
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)
Site 10
Farm 6Site 10
Malabar
Figure 18
Page 26
0 50 100 150 200Days
0
0.5
1
1.5
2
2.5
Nitr
ate-
N p
er A
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)
Site 11Site 12Site 13
Farm 7Sites 11, 12, and 13
Gainesville
Seffner
Lake
Figure 19
Page 27
0 50 100 150 200Days
0
0.1
0.2
0.3
0.4
0.5
0.6
Nitr
ate-
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er A
(lbs
)
Site 14
Farm 8Site 14
Ona
Figure 20
Page 28
0 50 100 150 200Days
0
0.5
1
1.5
2
2.5
Nitr
ate-
N p
er A
(lbs
)
Site 15Site 16
Farm 9Sites 15 and 16
Candler
Ft. Meade
Figure 21
Page 29
0 50 100 150 200Days
0
1
2
3
4
5
6
Nitr
ate-
N p
er A
(lbs
)
Site 17Site 18Site 19
Farm 10Sites 17, 18, and 19
Seffner
St. Johns
Ona
Figure 22
Page 30
0 50 100 150 200Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N p
er A
(lbs
)
Site 20
Farm 11Site 20
Myakka
Figure 23
Page 31
0 50 100 150 200Days
0
5
10
15
20
Nitr
ate-
N p
er A
(lbs
)
Site 1Site 2Site 3Site 4Site 5Site 6Site 7Site 8Site 9Site 10
Site 11Site 12Site 13Site 14Site 15Site 16Site 17Site 18Site 19Site 20
All Sites
Figure 24
Page 32
2005-2006 Progress Report This is the annual progress report for Year 2 of the project. Overall, all the objectives that were planned were met for the second year of this study. It was initiated in August 2005, by re-identifying existing grower/cooperators who: 1) had production fields containing specific soil types 2) were willing to share specific cultural management information 3) would allow water quality samples to be collected from production fields on a weekly basis. Sampling sites more than doubled from the 2004-05 season and cooperative agreements were arranged with grower/cooperators and monitoring equipment were installed. Figures 1-12 (2004-05 season section) show the sampling locations by farm overlaid on an aerial photo and soil map. A modified shorter design of the passive wick sampler (to facilitate easier and less destructive installation procedure) was used and compared at each sampling site. Figure 13 (2004-05 section) shows a cross-sectional diagram of the original sampler which uses fiberglass rope to break tension in soil column and cause accumulated water to move into the collection chamber. The leached water is then collected by suctioning out through the access tube and subsequently analyzed for nitrate-N content. Figure 25 shows the high degree to which the sampler has shown to be effective on different soils, but particularly effective on sandy soils. A detailed description for the operational theory for the sampler can be found at: http://www.regional.org.au/au/asssi/supersoil2004/s15/oral/1627_geeg.htm. A weekly water sampling scheme for strawberry production was implemented in November 2005 and continued through March 2006. Once strawberry production ceased, sampling continued at those locations where a double crop (i.e. melons, peppers, etc) was planted to follow the strawberries through May. As resulted from a survey of cooperators, generally, for a projected 120-day strawberry crop, producers were applying 0 to 30 lbs N as dry pre-plant fertilizer and 0.75-1.5 lbs N applied as liquid fertilizer per day. Irrigation applications ranged from 45 min/day to 3 hr/day depending on emitter flow rate and grower preference. However the majority of producers were applying irrigation water at 60 min/day. Fertilizer was injected at mid- to late-irrigation cycle with enough time left to flush the system before the irrigation cycle concluded. Specifically, the following general conclusions resulted from the responses to the survey: 1) growers use drip irrigation with overhead sprinklers for transplant
establishment and cold protection 2) crops are planted mid to late October 3) growers use at least five different microirrigation tube types amongst the
responses 4) growers use drip tube with 0.24 to 0.50 gpm/100 ft application rates 5) growers apply irrigation rates from 0.12 to 0.26 inches/A/day
Page 33
6) ~ 50% of growers apply no dry pre-plant fertilizer 7) growers that do apply dry pre-plant fertilizer apply ~ 20 to 40 lb N per acre 8) growers apply ~ 1 lb N per acre per day liquid fertilizer 9) growers use experience to decide when and how much to irrigate (with a
limited number using soil moisture measurements) 10) growers fertigate at the end of the cycle with ~15 to 30 flush time. Soil types of the sites identified included Immokalee, Pomello, St. Johns, Seffner, Zolfo, Kesson, Ona, Taveres, Malabar, Lake, Gainesville, Candler, Fort Meade, and Myakka. All sites had dry season water table levels below 2 m, so the sampling procedures used the passive “wick”-type leachate collector. As stated earlier, a smaller collector was developed and evaluated. These collectors allowed for collection of water and nutrients leaching below the crop rooting zone and allowed an estimated of mass balance losses of N and water from the fields. Figures 26-28 show the weekly losses for each sampling site at each farm. Remarkably, the results are very similar to the 2004-2005 results for specific farms. The results show that for the vast majority of sites, less than one lb/week was being leached with very few exceptions. Figure 29 show the seasonal weekly losses for all sampling sites. These figures support the minimal weekly leaching that was occurring at all grower/cooperator locations. The modified sampler that was used this season was used in addition to the original samplers, thus, each sampling site had 8 samplers. Figures 30-32 show the comparison of samplers. A statistical analysis to compared the samplers’ performance showed no difference for the sampling season. Seasonal cumulative nitrate-N losses for each site (with soil identified) at each farm are shown in Figures 33 through 44 (scales for each figure may differ). The figures show that for seasonal accumulated leaching losses of nitrate-N, only Farm 1 had losses exceeding 5 lbs/A and most were 2 lbs/A or less. Assuming a total seasonal application of 150 lbs/A, less than 10% losses occurred. Figure 45 summarizes the seasonal cumulative results for all sites. When compared to Figure 46 (2004-2005 cumulative results) it is remarkably evident that consistent and effective water and nutrient management practices are being used by the participants in the study and they seem to be doing an exceptional job of minimizing water and nutrient losses during the production season. Information from this first year of data collection was presented at the Florida Strawberry Growers Association’s Agritech 2006 meeting. These results are so consistent with the 2004-2005 results that very few modifications to existing practices are warranted. Although the results reflect the practices of the project participants only, this information is extremely valuable to the industry as a whole and provides evidence that grower participation in the state’s BMP implementation program should be encouraged and will involve very few modifications to existing practices.
Page 34
Figure 25
Water flux efficiency ratios (Jm/Ja) for 3a) sand, 3b) silt loam, and 3c) clay soils under a variety of steady-flux conditions and diversion barrier heights (Gee et al. 2004. SuperSoil2004: 3rd Australian New Zealand Soils Conference, 5 – 9 December 2004, University of Sydney, Australia.)
Page 35
Farm 1
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 1Site 2Site 3
Farm 2
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 4Site 5Site 6
Farm 3
0
1
2
3
4
5
0 40 80 120
Days
NO
3 / N
O2 N
(lb/
ac)
Site 7
Farm 4
0
1
2
3
4
5
0 40 80 120
Days
NO
3 / N
O2 N
(lb/
ac)
Site 8
Figure 26
Page 36
Farm 5
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 9
Farm 6
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 10
Farm 7
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 11Site 12Site 13
Farm 8
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 14
Figure 27
Page 37
Farm 9
0
1
2
3
4
5
0 40 80 120
Days
NO
3 / N
O2
N (lb
/ac)
Site 15Site 16
Farm 10
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 17Site 18Site 19
Farm 11
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 20
Farm 12
0
1
2
3
4
5
0 40 80 120Days
NO
3 / N
O2 N
(lb/
ac)
Site 21
Figure 28
Page 38
0
1
2
3
4
5
0 20 40 60 80 100 120Days
Nitr
ate-
N lo
ss (l
bs/a
c)
123456789101112131415161718192021
Site #
Figure 29
All sampling sites 2005-2006
Page 39
Site 1
0
1
2
3
4
5
0 40 80 120
Days
NO3
/ NO
2 N
(lb/
ac)
LargeSmall
Site 2
0 40 80 120
Days
Site 3
0 40 80 120
Days
Site 4
0 40 80 120
Days
Site 5
0
1
2
3
4
5
0 40 80 120
Days
NO3
/ NO
2 N
(lb/
ac)
LargeSmall
Site 6
0 40 80 120
Days
Site 7
0 40 80 120
Days
Site 8
0 40 80 120
Days
Figure 30
Comparison of performance of large samplers to small samplers
Page 40
Site 9
0
1
2
3
4
5
0 40 80 120
Days
NO
3 / N
O2 N
(lb/
ac)
LargeSmall
Site 10
0 40 80 120
Days
Site 11
0 40 80 120
Days
Site 12
0 40 80 120
Days
Site 13
0
1
2
3
4
5
0 40 80 120
Days
NO
3 / N
O2
N (l
b/ac
)
LargeSmall
Site 14
0 40 80 120
Days
Site 15
0 40 80 120
Days
Site 16
0 40 80 120
Days
Figure 31
Comparison of performance of large samplers to small samplers
Page 41
Site 17
0
1
2
3
4
5
0 40 80 120
Days
NO
3 / N
O2 N
(lb/
ac)
LargeSmall
Site 18
0 40 80 120
Days
Site 19
0 40 80 120
Days
Site 20
0
1
2
3
4
5
0 40 80 120
Days
NO3
/ NO
2 N
(lb/
ac)
LargeSmall
Site 21
0 40 80 120
Days
Figure 32
Comparison of performance of large samplers to small samplers
Page 42
Farm 1
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
2
4
6
8
10
12
14
Nitr
ate-
N L
oss
per A
(lbs
)
Site 1
Site 2
Site 3
Figure 33
St. Johns
Immokolee
Pomello
Seasonal N-losses (Cumulative)
Page 43
Farm 2
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.5
1
1.5
2
2.5
Nitr
ate-
N L
oss
per A
(lbs
)
Site 4
Site 5
Site 6
Figure 34
St. John’s
Seffner
Zolfo
Seasonal N-losses (Cumulative)
Page 44
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.2
0.4
0.6
0.8
1
Nitr
ate-
N L
oss
per A
(lbs
)
Site 7
Farm 3
Figure 35
Kesson
Seasonal N-losses (Cumulative) Page 45
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.1
0.2
0.3
0.4
Nitr
ate-
N L
oss
per A
(lbs
)
Site 8
Farm 4
Figure 36
Ona
Seasonal N-losses (Cumulative)
Page 46
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.05
0.1
0.15
0.2
0.25
Nitr
ate-
N L
oss
per A
(lbs
)
Site 9
Farm 5
Figure 37
Taveres
Seasonal N-losses (Cumulative) Page 47
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
1
2
3
4
5
Nitr
ate-
N L
oss
per A
(lbs
)
Site 10
Farm 6
Figure 38
Malabar
Seasonal N-losses (Cumulative) Page 48
Farm 7
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.5
1
1.5
2
2.5
Nitr
ate-
N L
oss
per A
(lbs
)
Site 11
Site 12
Site 13
Figure 39
Gainesville
Seffner
Lake
Seasonal N-losses (Cumulative) Page 49
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N L
oss
per A
(lbs
)
Site 14
Farm 8
Figure 40
Ona
Seasonal N-losses (Cumulative) Page 50
Farm 9
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.25
0.5
0.75
Nitr
ate-
N L
oss
per A
(lbs
)
Site 15
Site 16
Figure 41
Candler
Ft. Meade
Seasonal N-losses (Cumulative) Page 51
Farm 10
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.5
1
1.5
Nitr
ate-
N L
oss
per A
(lbs
)
Site 17
Site 18
Site 19
Figure 42
Seffner
St. Johns
Ona
Seasonal N-losses (Cumulative) Page 52
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.5
1
1.5
2
Nitr
ate-
N L
oss
per A
(lbs
)
Site 20
Farm 11
Figure 43
Seasonal N-losses (Cumulative)
Page 53
18
1522
2936
4350
5764
7178
8592
99106
113120
Days
0
0.5
1
1.5
2
Nitr
ate-
N L
oss
per A
(lbs
)
Site 21
Farm 12
Figure 44
Zolfo
Seasonal N-losses (Cumulative)
Page 54
0 20 40 60 80 100 120 140Days
0
5
10
15
Nitr
ate-
N L
oss
per A
(lbs
)
Site 1Site 2Site 3Site 4Site 5Site 6Site 7Site 8Site 9Site 10Site 11Site 12Site 13Site 14Site 15Site 16Site 17Site 18Site 19Site 20Site 21
All Sites (2005-2006)
Figure 45
Seasonal N-losses (Cumulative)
Page 55
0 50 100 150 200Days
0
5
10
15
Nitr
ate-
N L
oss
per A
(lbs
)
Site 1Site 2Site 3Site 4Site 5Site 6Site 7Site 8Site 9Site 10Site 11Site 12Site 13Site 14Site 15Site 16Site 17Site 18Site 19Site 20
All Sites (2004-2005)
Figure 46
Seasonal N-losses (Cumulative) Page 56
2006-2007 Progress Report This is the annual progress report for Year 3 of the project. Overall, all the objectives that were planned were met for the third year of this study. It was initiated in August 2006, by re-identifying existing grower/cooperators who: 1) had production fields containing specific soil types 2) were willing to share specific cultural management information 3) would allow water quality samples to be collected from production fields on a weekly basis. The sampling locations were the same as previous seasons (Figures 1-12). A weekly water sampling scheme for strawberry production was implemented in November 2006 and continued through March 2007. Once strawberry production ceased, sampling continued at those locations where a double crop (i.e. melons, peppers, etc) was planted to follow the strawberries through May. A grower survey to ascertain the production inputs and management practices of the grower cooperators was implemented. The results of the survey showed some variability in management practices, but nothing extremely divergent among sites. Generally, for a projected 120-day strawberry crop, producers were applying 0 to 30 lbs N as dry pre-plant fertilizer and 0.75-1.5 lbs N applied as liquid fertilizer per day. Irrigation applications ranged from 45 min/day to 3 hr/day depending on emitter flow rate and grower preference. However the majority of producers were applying irrigation water at 60 min/day. Fertilizer was injected at mid- to late-irrigation cycle with enough time left to flush the system before the irrigation cycle concluded. Specifically, the following general conclusions resulted from the responses to the survey: 1) growers use drip irrigation with overhead sprinklers for transplant
establishment and cold protection 2) crops are planted mid to late October 3) growers use at least five different microirrigation tube types amongst the
responses 4) growers use drip tube with 0.24 to 0.50 gpm/100 ft application rates 5) growers apply irrigation rates from 0.12 to 0.26 inches/A/day 6) ~ 50% of growers apply no dry pre-plant fertilizer 7) growers that do apply dry pre-plant fertilizer apply ~ 20 to 40 lb N per acre 8) growers apply ~ 1 lb N per acre per day liquid fertilizer 9) growers use experience to decide when and how much to irrigate (with a
limited number using soil moisture measurements) 10) growers fertigate at the end of the cycle with ~15 to 30 flush time. Soil types of the sites identified included Immokalee, Pomello, St. Johns, Seffner, Zolfo, Kesson, Ona, Taveres, Malabar, Lake, Gainesville, Candler, Fort Meade, and Myakka. All sites had dry season water table levels below 2 m, so the
Page 57
sampling procedures used the passive “wick”-type leachate collector. As stated earlier, a smaller collector was developed and evaluated. These collectors allowed for collection of water and nutrients leaching below the crop rooting zone and allowed an estimated of mass balance losses of N and water from the fields. The results for the seasonal monitoring are shown in Figures 47 through 63. Remarkably, the results are very similar to the results from the previous 2 years for specific farms. Figure 47 shows the nitrate-N leached at any particular site for each sampling date. The results show that for the vast majority of sites, less than one lb/week was being leached with very few exceptions. Figures 48-50 show the weekly losses for each sampling site at each farm. These figures support the minimal weekly leaching that was occurring at all grower/cooperator locations. Seasonal cumulative nitrate-N losses for each site (with soil identified) at each farm are shown in Figures 51 through 62 (scales for each figure may differ). The figures show that for seasonal accumulated leaching losses of nitrate-N, only Farm 1 had losses exceeding 5 lbs/A and most were 2 lbs/A or less. Assuming a total seasonal application of 150 lbs/A, less than 10% losses occurred. Figure 63 summarizes the seasonal cumulative results for all sites. When compared to Figures 64 and 65 (2004-2005 and 2005-2006 cumulative results, respectively) it is remarkably evident that consistent and effective water and nutrient management practices are being used by the participants in the study and they seem to be doing an exceptional job of minimizing water and nutrient losses during the production season. These results are so consistent with the 2004-2005 and 2005-2006 results that very few modifications to existing practices are warranted. Although the results reflect the practices of the project participants only, this information is extremely valuable to the industry as a whole and provides evidence that grower participation in the state’s BMP implementation program should be encouraged and will involve very few modifications to existing practices.
Page 58
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.5
1
1.5
2
2.5
3
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
) 1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
All Sites
Figure 47
Page 59
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.5
1
1.5
2
2.5
3
Nitr
ate-
N lo
ss (#
/A)
123
Farm 1
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N lo
ss (#
/A)
456
Farm 2
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N lo
ss (#
/A)
7
Farm 3
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N lo
ss (#
/A)
8
Farm 4
Figure 48
Page 60
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N lo
ss (#
/A)
9
Farm 5
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
1
2
3
4
5
Nitr
ate-
N lo
ss (#
/A)
10
Farm 6
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.5
1
1.5
2
2.5
3
Nitr
ate-
N lo
ss (#
/A)
111213
Farm 7
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N lo
ss (#
/A)
14
Farm 8
Figure 49
Page 61
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.2
0.4
0.6
0.8
1
Nitr
ate-
N lo
ss (#
/A)
1516
Farm 9
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N lo
ss (#
/A)
171819
Farm 10
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Nitr
ate-
N lo
ss (#
/A)
20
Farm 11
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.2
0.4
0.6
0.8
1
Nitr
ate-
N lo
ss (#
/A)
21
Farm 12
Figure 50
Page 62
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
2
4
6
8
10
12
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 1
Site 2
Site 3
Farm 1
St. Johns
Immokolee
Pomello
Figure 51
Page 63
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 4
Site 5
Site 6
Farm 2
St. John’s Seffner
Zolfo
Figure 52
Page 64
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 7
Farm 3
Kesson
Figure 53
Page 65
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 8
Farm 4
Ona
Figure 54
Page 66
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 9
Farm 5
Taveres
Figure 55
Page 67
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
1
2
3
4
5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 10
Farm 6
Malabar
Figure 56
Page 68
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.5
1
1.5
2
2.5
3
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 11
Site 12
Site 13
Farm 7
Gainesville
SeffnerLake
Figure 57
Page 69
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 14
Farm 8
Ona
Figure 58
Page 70
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.5
1
1.5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 15
Site 16
Farm 9
Candler
Ft. Meade
Figure 59
Page 71
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
0.6
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 17
Site 18
Site 19
Farm 10
Seffner
St. Johns
Ona
Figure 60
Page 72
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
0.1
0.2
0.3
0.4
0.5
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 20
Farm 11
Figure 61
Page 73
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
)
Site 21
Farm 12
Zolfo
Figure 62
Page 74
117
3443
4957
6270
7784
95102
112118
125134
140146
154
Days
0
2
4
6
8
10
12
Cum
ulat
ive
Nitr
ate-
N L
oss
(#/A
) 1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
All Sites (2006-2007)
Figure 63
Page 75
0 50 100 150 200Days
0
5
10
15
Nitr
ate-
N L
oss
per A
(lbs
)
Site 1Site 2Site 3Site 4Site 5Site 6Site 7Site 8Site 9Site 10Site 11Site 12Site 13Site 14Site 15Site 16Site 17Site 18Site 19Site 20
All Sites (2004-2005)
Figure 64
Page 76
0 20 40 60 80 100 120 140Days
0
5
10
15
Nitr
ate-
N L
oss
per A
(lbs
)
Site 1Site 2Site 3Site 4Site 5Site 6Site 7Site 8Site 9Site 10Site 11Site 12Site 13Site 14Site 15Site 16Site 17Site 18Site 19Site 20Site 21
All Sites (2005-2006)
Figure 65
Page 77
Discussion - All seasons combined Overall, there was little seasonal variability of nitrate-N leached from each site at each farm. Individual farm irrigation and nutrient management likely influenced the overall leached N compared to other farms, but soil type may have influence leaching for those farms where similar management intensity occurred regardless of soil type. For example, Farms 1 and 7 had 3 soil types each and there were fairly consistent leaching differences among soil types on each farm over the three seasons. While these differences existed, the magnitude of these differences probably doesn’t warrant large scale management changes due to soil type. Figure 66 shows the average seasonal cumulative leaching for each year (all sites on all farms). Differences among seasons were always less than 0.5 lbs of N at any time indicating the repeatability of the results from year to year. When one considers the considerable variability that can be experienced when conducting such a study on commercial production fields, the results from this study are remarkable. However, when one considers the BMP’s that strawberry producers are currently implementing, the results should not be surprising. All of the growers in this study (and up to 95% of the industry) use microirrigation as the means of providing water and nutrient to their crop. Because strawberries are very prone to salt damage, producers accepted microirrigation many years ago primarily because of its ability to provide liquid fertilizer when and where is it needed. The water conservation advantages of microirrigation were secondary. Because accumulated fertilizer salts are to be avoided, producers are careful not too over-apply N, and because irrigation management goes hand-in-hand with nutrient management, care is taken to not to leach the applied nutrients below the root zone. The survey of cooperators showed that 50% of the sites received no pre-plant dry N fertilizer and where it was applied, only an average of 31 lbs N was used. This lack of pre-plant dry fertilizer also shows the reliance on microirrigation applied fertilizer and the care necessary to do it right. In conclusion, it appears that for the cooperators participating in this study, current strawberry production practices are adequate for managing nitrate-N losses from production fields. It would be assumed that the conclusion could be drawn for other growers using similar management practices.
Page 78
0 50 100 150 200Days
0
0.5
1
1.5
2
2.5
Nitr
ate-
N lo
ss (#
/A)
2004-052005-062006-07
Average Nitrate-N Loss By SeasonBy Season(all sites and farms combined)
Page 79