Making Turf The Best It Can Be; Good Nutrition and Good Environment. Marty Petrovic, Ph.D. Section of Horticulture Cornell University

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Transcription:

Making Turf The Best It Can Be; Good Nutrition and Good Environment Marty Petrovic, Ph.D. Section of Horticulture Cornell University

How do you measure a fertilizer response in a turf setting?

How do you measure a fertilizer response in a turf setting?

How do you measure a fertilizer response in a turf setting? Aesthetics characteristics: color: dark green shoot density: dense uniformity: consistent

How do you measure a fertilizer response in a turf setting? Aesthetics characteristics: Functional characteristics: * withstand traffic stress (wear, compaction) * recuperate from damage( insects, diseases, traffic, heat/drought /cold) * remain dense to prevent erosion and runoff

How do you measure a fertilizer response in a turf setting? Aesthetics characteristics: Functional characteristics: Growth or yield: not directly! Unless you are in seed or sod production

Why must nutrients be applied? Nutrient fate-gasous loss Plants remove nutrients leave the system Nutrients become unavailable Nutrients leach or runoff leave the system Apply when plant demand >> plant avail.

Nitrogen

It s Hockey Time, thank God!!! Two most hated things: Other teams goalie (sieve) Refs

Cornell Hockey Cheer I am Blind, I am Deaf, I want to be a ref!!!

Role of Nitrogen Required in high amounts in tissue: 2 to 6% of N, dry weight Vital roles: chlorophyll, amino acids, proteins, nucleic acids, enzymes and vitamins Affects on shoot and root growth, density, color, and tolerance/recovery from stresses

Clippings lb/m Turf s Perpetual Hunger for N 450 400 350 300 250 200 150 100 50 0 0 5 10 15 20 N Rate lb/m/yr

Factors affecting nitrogen recovery in the turfgrass plant Nitrogen status of the plant

From Bowman & Paul, 1988) Nitrogen status of the plant Slightly deficient turf can utilize more nitrogen

Factors affecting nitrogen recovery in the turfgrass plant Nitrogen status of the plant Timing of application (season)

Timing of application (for cool-season grasses)

Factors affecting nitrogen recovery in the turfgrass plant Nitrogen status of the plant Timing of application (season) Clipping management

Clipping management When clipping returned: equal amount of N found in the plant from clipping recycling, soil and fertilizer N. When clipping removed: half of N in plant from soil and half from fertilizer N. Up to 25% more N is needed when clipping are removed. From Starr & De Roo (1981), Kentucky bluegrass/ fine fescue turf fertilized with 15 N ammonium sulfate

Factors affecting nitrogen recovery in the turfgrass plant Nitrogen status of the plant Timing of application (season) Clipping management Species and cultivar differences

Species and cultivar differences If you gave grass all the N they could use, how much would they take up? Species range* Average Kentucky blue 4-6 5.1 Perennial rye 4-9 7.2 Tall fescue 4-7 5.4 * mmoles N/ g/hr From Liu et. al., 1993)

Factors affecting nitrogen recovery in the turfgrass plant Nitrogen status of the plant Timing of application (season) Clipping management Species and cultivar differences Nitrogen source

Nitrogen source % recovered Nitrogen Source in clippings Solubility Urea, am. Sulfate 48 high Methylene urea 42 IBDU 47 Biosolid (Milorganite) 29 Ureaformaldehyde 22 low From Hummel & Waddington, 1981, Kentucky bluegrass

Factors affecting nitrogen recovery in the turfgrass plant Nitrogen status of the plant Timing of application (season) Clipping management Species and cultivar differences Nitrogen source Soil and age

Soil Soil texture clipping soil (roots) leachate ----------- % of applied N ------- Sand 8 82 10 Sandy loam 52 45 3 Silt loam 92 6 2 Petrovic (2004) creeping bentgrass fairway turf

Total N (kg/ha) Soil and age Total soil N 3000 2500 2000 1500 2 lbs N/1000 sq.ft/ yr stored in soil 1000 500 0 0 yr. 5 yr. 10 yr. 15 yr. 20 yr. 25.yr. 30 yr. 40 yr. 50.yr. age of turfgrass site

Nitrogen Fertilization Program Nitrogen Sources

Nitrogen Sources QUICK RELEASE soluble, readily available MODERATE RELEASE some readily available SLOW RELEASE water insoluble, coated, slowly available, controlled release

MODERATE RELEASE sulfur coated urea IBDU on acid soils some natural organic sources methylene urea

CHARACTERISTICS OF MODERATE RELEASE N moderate initial response some extended response less leaching potential than quickly available sources moderate to high costs

CHARACTERISTICS OF SLOW RELEASE NITROGEN FERTILIZERS extended availability applied at higher rates less frequently low solubility minimal environmental losses low initial availability

Natural Organic Fertilizers processed by-products of animal production: dried blood, bone meal, manure, feather meal, bio-solids, fish plant by-products: cotton seed meal, corn gluten meal

ADVANTAGES OF NATURAL ORGANIC FERTILIZERS low chance of foliar burn potential little risk of N leaching groundwater contain both macro and micronutrients improve soil microbial activity

ADVANTAGES OF NATURAL ORGANIC FERTILIZERS some disease suppression potential to reduce thatch long term improvement in soil properties

DISADVANTAGE OF NATURAL ORGANIC FERTILIZERS low nitrogen analysis high cost per pound of nitrogen blended not homogenized may apply nutrients when not needed could lead to P runoff cost of labor - application

DISADVANTAGE OF NATURAL odor ORGANIC FERTILIZERS difficult to handle availability of nutrients depends on temperature limited cool season response uniformity of application inconsistent nutrient release and turf response

Challenges of an Organic Soil Fertility Program Most of the nutrients are released by microbial activity (limited by temperature and moisture)

Slow-release Fertilizers Natural/Organic fertilizers Coated fertilizers Uncoated fertilizers

Slow-release: General information Release rates vary Weeks to years Release mechanisms dependent on Temperature Soil Moisture ph

Fertilizer Source What happens to the release when Temp is low Temp is high ph is low (<5) Soil Moisture is low Soil Moisture is high

Fertilizer Source What happens to the release when Temp is low Temp is high ph is low (<5) Soil Moisture is low Soil Moisture is high Inorganics and urea Same Same Same Can burn Can leach Natural organic Same

Fertilizer Source What happens to the release when Temp is low Temp is high ph is low (<5) Soil Moisture is low Soil Moisture is high Inorganics and urea Same Same Same Can burn Can leach Natural organic Same Synthetic organic (UF, MU) Same

Fertilizer Source What happens to the release when Temp is low Temp is high ph is low (<5) Soil Moisture is low Soil Moisture is high Inorganics and urea Same Same Same Can burn Can leach Natural organic Same Synthetic organic (UF, MU) Same Sulfur coated N Same Same Same Same

Fertilizer Source What happens to the release when Temp is low Temp is high ph is low (<5) Soil Moisture is low Soil Moisture is high Inorganics and urea Same Same Same Can burn Can leach Natural organic Same Synthetic organic (UF, MU) Same Sulfur coated N Same Same Same Same Polymer coated N Same Same

Fertilizer Source What happens to the release when Temp is low Temp is high ph is low (<5) Soil Moisture is low Soil Moisture is high Inorganics and urea Same Same Same Can burn Can leach Natural organic Same Synthetic organic (UF, MU) Same Sulfur coated N Same Same Same Same Polymer coated N Same Same IBDU Same Same Same

Fertilizer Source Inorganics and urea Release rate under optimal conditions 1 3 weeks Natural organic Sulfur coated N Polymer coated N Ureaform Methylene Ureas MDU/DMTU IBDU 1 6 months 1 2 months Variable (weeks to all year) 1 2 years 2 4 months 1 2 months 1 4 months

Nitrogen Fertilization Program Nitrogen Sources Standard program of Application

Nitrogen Fertilization Program for Ontario Lawns Late Early Late Late # of yearly apps Spring Summer Summer Fall 1 - - X - 2 X - X - 3 X - X X 4 X X X X X= application at 0.5 kg N/100 sq. M

Nitrogen Fertilization Program Nitrogen Sources Standard Program of Application Single application rates water soluble sources: trace (fertigation) spray: 0.1-0.7 lb. N/1000 sq.ft dry: up to 0.7 lb. N/1000 sq.ft. Slow release: 0.5-2.5 lbs. N/1000 sq.ft High (2.5lbs N/1000 sq.ft.) in spring

Nitrogen Fertilization Program Single application rates water soluble sources: sands up 0.4 lbs N/1,000 sq.ft Others soils: up to 0.7 lbs N/1,000 sq.ft. Any more there is too much N leaching!!!

Lbs of N (per 1000 sq ft) Leached 0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 1.1 1.2 1.3 1.4 1.5 1.6 1.4 1.2 1 0.8 0.6 0.4 0.2 0 Study results: Average Soluble N leached 7 Days after application for Kentucky bluegrass Sand Sandy Loam Lbs Soluble N per 1000 sq ft Applied

Nitrogen Fertilization Program Nitrogen Sources Standard Program of Application Single application rates Soil and Tissue testing

Soil and Tissue testing Soil testing for N: not done for turf, why? Tissue testing: sufficiency range Grass % N Bermudagrass 4.0-6.0 Creeping bentgrass 4.5-6.0 Perennial ryegrass 3.3-5.1 St. Augustinegrass 1.9-3.0 From Mills and Jones, 1996 Tissues testing often coupled with fertigation

Nitrogen application methods Fertilized during half time?

Nitrogen application methods Love the technique!!!

Keep it on the lawn

Phosphorus

Don t you just love the refs!

Source: Mississippi State Extenstion

The Primary Macros: Phosphorus Functions ATP energy currency of the cell Membrane components DNA components Deficiency symptoms Reduced growth Dark, purple color

Phosphorus deficient corn

The Primary Macros: Phosphorus Management P very insoluble in soil Availability is a function of root surface area During establishment root system is not extensive, therefore P is not readily available and fertilizer will speed growth After root system is established responses to P rarely seen and deficiencies (purple color are even more rare)

From: Christians, 2003

The Primary Macros: Phosphorus Management P availability is also sensitive to ph Maximum P availability in soil is at ph 6.5

Phosphorus Fertilizer Sources Rock Phosphate Primary Mineral Apatite Ca 10 F 2 (PO 4 ) 6 P availability can vary from 0-5-0 to 0-17-0 Superphosphate (0-20-0) Rock phosphate treated with sulfuric acid (also sulfur and calcium source)

Phosphorus Fertilizer Sources Triple superphosphate (0-46-0) Rock phosphate treated with phosphoric acid (also calcium source) Ammoniated phosphates Phosphoric acid treated with NH 3 Monoammonium phosphate (MAP) 11-48-0 Diammonium phosphate (DAP) 18-46-0 Most Natural organics-can be high in P compared to N

Potassium

The Primary Macros: Potassium Functions Water regulation Cell growth Opening and closing of stomata Activates enzymes Regulates cell ph Deficiency symptoms Reduced growth Yellow leaf margins

Potassium deficiency in corn

The Primary Macros: Potassium Management K held on cation exchange sites in soil Recent research suggests turfgrass requires less potassium than previously thought What has been said of K. Improves drought tolerance Improves cold hardiness Increases rooting Resistance to dollar spot Wear tolerance

Potassium-suppression of germination Turner, 1980

Potassium Fertilizer Sources Potash burn wood, leach ashes with water and evaporate water to get K salts, mostly K 2 CO 3 (natural) Most K fertilizers are taken from salt mines (natural if minimally processed) KCl potassium chloride muriate of potash (0 0 60) Inexpensive High Salt Index

Potassium Fertilizer Sources K 2 SO 4 potassium sulfate sulfate of potash (0 0 50) Lower salt index For establishment look for this source KNO 3 potassium nitrate (13 0-44) or calcium nitrate (Chelian nitrate) Very high salt index! Expensive, specialty use only Limited organic forms

Summary of the big 3 Nitrogen management is extremely important Phosphorus is important at establishment Potassium is of less importance than we thought although continue to maintain soil test levels

Soil Testing Soil Sampling

There is a lot of love between hockey players!

Soil Testing Why?

Why do we care? Soil chemical testing: is part of a fertilization program, determine the amount of nutrients (especially phosphorus, potassium, ) and lime/sulfur needed to produce a healthy turfgrass stand.

Why do we care? Soil testing: Can be used to diagnose problems related to nutrients, salts and soil ph. Organic matter level, does the soil need more organic matter or N release?

Soil testing: Why do we care? also may be used as a best management practices to reduce the risk of phosphorus runoff and protect the environment. Many state law, local laws

What does a soil test do? Measures the amount of nutrients readily available (in soil water) and what can be supplied by the soil during a growing season (reserve).

Why does a soil test do? Readily available-supplies a 1-2 days The amount of reserve nutrients is based on: -parent material (K, Ca, Mg ) -cation exchange capacity-clay and organic matter -ph

Nutrient reservoir: Cation exchange capacity Humus Humus or clay or clay - - - - - - - Ca++ - Mg ++ - K + Ca ++ K + Mg ++ Soil solution

What does a soil test do? Amount of nutrients found based on extraction method- Water or weak salt- only what is in the soil solution Acids: the stronger the acid more reserve nutrients are measured Amount may vary from lab to lab!!

Where do soil test work best? Soils with a CEC above 6 (meq/100 g Non-sandy soils! or cmol/kg)

Where do soil test work best? Soils with a CEC above 6 (meq/100 g Non-sandy soils! or cmol/kg)

Soil sampling

PROPER SOIL SAMPLING is the key! Follow the direction from the lab use a tool that can do the job remove thatch and plant debris sample at a uniform depth take 15-20 samples from a uniform area (composite sample) half pint is needed mix in plastic bag or plastic bucket

BEST TIME FOR SAMPLING before planting allow time to get results back sample same time each year, Sample every 2 or 3 years unless you have a problem If possible, wait 2-4 weeks after applying fertilizer before sampling

FOR THE BEST RECOMMENDATION Take a good representative sample provide detailed background information

Turfgrass and the environment: how to best manage it

Someone having a bad day?

Phosphorus Management Produce dense plant to reduce runoff (keep out sparse weeds, insects and diseases). A proper N fertilization program is essential!

Phosphorus Management Dense turf reduce runoff Avoid treating impervious surfaces (driveways, sidewalks and roads don t need to be fertilized!!)

Keep it on the lawn

Phosphorus Management Dense turf reduce runoff Avoid treating impervious surfaces A good fertilization program often reduces runoff by increasing plant density and water infiltration rate

Phosphorus Management Dense turf reduce runoff Avoid treating impervious surfaces Fertilization often reduces P runoff, soil test to determine P need Soil testing for P level, apply only when needed!

Phosphorus Management Dense turf reduce runoff Avoid treating impervious surfaces Fertilization often reduces P runoff Soil testing for P level be careful with animal composts, many contain high amounts of phosphorus (especially when used as a soil amendment)

Phosphorus Management Dense turf reduce runoff Avoid treating impervious surfaces Fertilization often reduces P runoff Soil testing for P level many not be an effective tool in reducing P runoff be careful with animal composts, many contain high amounts of phosphorus (especially when used as a soil amendment) Remove tree litter (leaves and flowering parts) from storm drain system

Phosphorus Management Dense turf reduce runoff Avoid treating impervious surfaces Fertilization often reduces P runoff Soil testing for P level be careful with animal composts, many contain high amounts of phosphorus Remove tree litter from storm drain system Use low P winter deicing materials

Phosphorus Management Dense turf reduce runoff Avoid treating impervious surfaces Fertilization often reduces P runoff Soil testing for P level many not be an effective tool in reducing P runoff Remove tree litter from storm drain system Use low P winter deicing materials check the P content of the salt and traction materials you are using

Nitrogen

What is he doing?

Management Options to Reduce Impacts from Nitrogen Sources Rates of application Timing-seasonality Irrigation Age of site with long term impacts

Management Options to Reduce Impacts:Nitrogen Sources-use slow release when possible- but only effective in reducing leaching in wet years

Management Options to Reduce Impacts:Nitrogen Sources-use slow release when possible Rates of application-low as practical (especially with water soluble fertilizers like urea)

Management Options to Reduce Impacts:Nitrogen Sources-use slow release when possible Rates of application-low as practical Timing-seasonality-caution in late fall (greatest time for N leaching if soils are unfrozen)

Management Options to Reduce Impacts:Nitrogen Sources-use slow release when possible Rates of application-low as practical Timing-seasonality-caution in late fall Irrigation-use water wisely, base on evapotranspiration (ET) values

Things you need to know on how to be a great environmental manager Maintain for dense planting! Know your site (soils, slopes, compaction, soil test levels, org. matter) Know your materials that you are using Follow IPM practices to better pest control and less pesticide use Think of the environment in your decision making process

Diseases suppressed by natural organic fertilizers and compost: Yellow patch Pink patch Pythium root rot Typhula blight (gray snowmold)

Nutrition and Pest Problems Low Nitrogen Annual grassy weeds Dollar spot Rust red thread Many broadleaf weeds Anthracnose High Nitrogen brown patch ground ivy snow mold leaf spot

Best Management Practices?

Good Practices

Questions?