Title: FORMS OF PHOSPHORUS IN THE SOIL
1FORMS OF PHOSPHORUS IN THE SOIL
- Inorganic (50-70 of soil P)
- Bound (Fixed)
- Bound to Al, Fe and Ca cations on soil clay
particles - Dependent on soil pH
- Binding cations Optimum pH
- Al, Fe
4 - 5 - Ca
7 8 - Most P in soil
- Binding occurs rapidly when any P is applied
- Most fixed in the upper 2 5 inches of soil
- Less P fixed in sandy or peaty soils with high
infiltration rates - Bound P is unavailable to plants
- Primarily pollutes water sources with soil
erosion - Available P (Labile)
- P that is not fixed or has been released from
bound P - Forms
- Orthophosphate (HPO4, H2PO4)
- Usually present in very low amounts
- Dependent on
2- Conversion of bound P to soil available P is a
slow process - Most soil tests measure available P, not total P
- Available P is water soluble
- May move with subsurface water flow to surface or
subsurface water resources - 60 90 of the P in animal manure is in an
inorganic available form - Organic P
- Bound
- P that is immobilized by microbial conversion of
organic P into more resistant and stable forms of
organic P - Increases with increasing CarbonPhosphorus
ratios - Greatest at CP ratios gt 3001
- Transported with soil erosion to water sources
- Available
- P in undecomposed plant residues and microbes
- Must be converted to inorganic P by microbial
mineralization before being used by plants - Available organic P is often water soluble
- Sources of dissolved organic P
- Decaying plant material
- Manure
- Transported with run-off or subsurface water
3FORMS OF PHOSPHORUS IN SOIL
4P FERTILITY
- Discussed as P2O5
- Calculated by multiplying P by 2.29
5P TRANSPORT IN THE ENVIRONMENT
- Forms
- Sediment P
- Includes
- Fixed inorganic
- Bound organic
- Transported with sediment associated with soil
erosion - Primary form lost from cultivated land or from
stream bank erosion in pastures - Slowly supplies P for algae growth in water
sources - Dissolved P
- Includes
- Available inorganic P
- Available organic P
- Amount increases with increasing P content of
soil - Transport by
- Surface run-off
- Subsurface flow and tile
- Primary form of P in run-off from land covered
with vegetation - Immediately available for algae growth
6P TRANSPORT IN THE ENVIRONMENT
7EFFECTS OF P ON ENVIRONMENTAL QUALITY
- Eutrophication of surface water sources
- Primary cause of eutrophication of fresh water
sources - Algae in fresh water sources can use atmospheric
N2 as N sources - P limits algae growth
- Recently identified as the major cause of the
hypoxic (dead) zone in the Gulf of Mexico - Effects
- Excessive growth of undesirable algae and plants
- Results in O2 shortage as algae and plants die
and decay - May result in blooms of cyanobacteria and harmful
algae like Pfiesteria piscida. - Results
- Summer fish kills
- Taste, odor and treatment problems in water
- Increased water turbidity
- Decreased recreational use
- P levels
- Eutrophication
.02 mg/l - Plant growth .2
- .3 mg/l - Water quality standards
- Streams entering lakes
.05 mg/l (50 ppb)
8P CONCENTRATION IN IOWA LAKES (2001)
9CHANGE IN THE CONCENTRATION OF P IN MAN-MADE
LAKES IN IOWA
10LIVESTOCK AND LOADING OF P IN THE ENVIRONMENT
- Concentration of livestock production
- 31 of farms in US have inadequate land to apply
P from the manure produced - Manure from these farms represents 70 of the
excess manure P produced - 5 of the counties have inadequate land to apply
P from the manure produced - Manure from these counties represents 23 of the
excess manure P
11- The low NP ratio of manure relative to crop
needs - Crop NP2O5 needed Livestock NP2O5
excreted NP2O5 available - Corn grain 2.5 Swine (G-F)
1.15 .88 (Slurry) - Soybeans 4.26 Beef feedlot
1.41 .75 (Scraped) - Alfalfa 4.5 Lactating dairy
cow 2.45 .88 (Slurry) - Bromegrass 3.88 Layer
1.15 .88 (Slurry) - Corn silage 1.95 Turkey
1.17 .75 (Litter) -
w/ incorporation - Results in excess P accumulation in soil if N is
applied at the agronomic rate - Problem is enhanced by N volatilization
12- Low P retention
-
retained - Growing cattle
21 - Growing swine
27 - Poultry
21 - Grazing cattle
- Little P removed by grazing cattle
- Most P is recycled to the soil
- Pastures generally are not good places to
repeatedly fertilize with swine and poultry
manure unless periodically baled - Stream bank erosion
- Poorly managed grazing may remove vegetation from
stream banks allowing soil erosion - With increasing soil erosion, P pollution of
streams will occur
13FUNCTIONS OF P IN LIVESTOCK
- Bone structure
- 80 of the bodys P
- Bound to calcium as hydroxyapatite crystals
- Ca10 x(PO4)6(OH)2(H3O)2x
- CaP ratio 21
- Serves as a reserve source for Ca and P for other
functions - Energy metabolism
- Adenosine triphosphate (ATP)
- Creatinine phosphate
- Genetic structure
- Nucleic acids
- Cell membranes and organelles
- Phospholipids
- Phosphoproteins
- Acid-base balance
- Microbial growth and digestion in the rumen of
ruminant animals
14P DEFICIENCY SYMPTOMS
- Bone abnormalities
- Weak, bent, easily broken
- In young animals, rickets
- In adult animals, osteomalacia
- Loss of appetite or depraved appetite
- Animals eat unusual materials like pebbles,
metals etc. - Behavior does not represent a sense for P in
feeds - Unthrifty appearance and loss of growth
- Reduced milk production
- In swine, paralysis of the hind limbs
- In cattle, reduced fertility
- Questionable concern
- Only occurs when cattle are fed very low P levels
(lt .2P) for long periods of time - May be the result of impaired feed digestion by
not meeting the microbial needs
15P IN FEEDS
- P concentration in feeds
- P concentration in most feeds except mature
forages is moderate to high. - Livestock species Total P reqt. Feed
class Feed P, DM - Dairy cow
- Lactating .40
Energy conc Corn .30 - Dry .25
Oats
.40 - Beef
Cottonseed
.60 - Finishing steer .24
Protein conc Soybean meal .71 - Lactating cow .22
Meat and bone 4.73 - Dry cow .12
Grain Wheat mids
1.02 - Swine
processing Distillers grains
.83 - Growing-finishing .4 - .6
byproducts Corn gluten feed1.00 - Sow .6
Forages Corn silage
.28 - Poultry
Alfalfa hay
.31 - Layers .4
Grass hay
.30 - Broilers .4
Grass pasture
.40 - Turkeys .6
Corn stalks
.09
16- Availability of P in feeds
- 60 75 of P in grains, grain by-products, and
oilseed meals is bound to form phytate - Phytate-phosphorus is unavailable to monogastric
animals - Phytate-phosphorus is degraded by the enzyme,
phytase, produced by the rumen bacteria in
ruminant animals
17- P availability
-
Swine and poultry Cattle -
( available) - Corn and corn byproducts 15
70 - Wheat
50 70 - Soybean meal
25 70 - Meat and bone meal
67 - - Forages
- 64 - Dicalcium phosphate
100 70 - Defluorinated phosphate
95 70 - Must compensate for the low availability of
phosphorus from plant sources in monogastrics by
supplementing mineral sources - Results in increase P excretion
18P DIGESTION AND METABOLISM IN NONRUMINANTS
- Small intestine
- Phytate-P
- (60-75 of plant P)
-
Excess Ca or high pH
Feces - Inorganic P
- Passive
Active -
absorption transport -
Circulating P
1,25(OH)2vitamin D -
kidney - Bone
(Low blood Ca or P) - Soft tissue
25 (OH) vitamin
D -
Excess (Circulating
in blood) -
Liver -
Kidney Vitamin D -
(Diet or
sunlight)
19- Factors affecting P absorption from the gut
- Phytate
- High phytate reduces P absorption
- CaP ratio
- CaP should be between 11 to 1.251
- Intestinal pH
- High intestinal pH reduces P absorption
- Vitamin D
- Vitamin D deficiency reduces P absorption
20STRATEGIES TO LIMIT P LOADING OF THE ENVIRONMENT
BY NONRUMINANT ANIMALS
- Increase availability of dietary P
- Degrade phytate-P
- Feed microbial phytase
- Enzyme produced by fungus, Aspergillus sp.
- Treatment
- 200 to 1000 units/kg
- 500 units 90 gm/ton
- Effects
- Decrease P excretion by 30 to 50
- Increases availability of some other minerals and
amino acids - Most activity occurs in stomach or gizzard
- Optimal activity occurs at pH lt4.0
- Effectiveness decreased if
- Excess Ca is fed
- Vitamin D is deficient
- Phytase is applied before pelleting feed
- Temperatures greater than 140 F destroys
enzyme - Effectiveness improved if
- Fed as an enzyme cocktail with phosphatase,
protease, citric acid, and pectinase
21- To reduce P excretion when using phytase, rations
must be balanced to meet the available P
requirement - Phytase can reduce the amount of inorganic P
supplemented in swine and poultry diets by .1
unit or 25 - Example (Swine)
1000 head Farrow-finish -
P in phases Manure P (lb P2O5/yr) - Normal diet .60,
.55, .50, .45 13,000 - Phytase-treated .50, .45,
.40, .35 8,900 - Economics of using phytase
- Cost of phytase cost of dicalcium phosphate
saved - Genetically modify crops to contain phytase
- Successful in corn and soybeans
- Limitations
- Susceptible to destruction from heating during
processing - Difficulty in separating genetically modified
crops from other varieties
22- Genetically modify swine to have phytase in
saliva - Gene from Escherichia coli has been inserted into
swine - Phytase secreted in saliva of GM pigs
- Stable at pH 2.5
- Resistant to pepsin
- Decreases P excretion by 60
- Limitations
- Variable response
- Regulator and consumer concerns with GMO foods
- Possible allergenicity to E. Coli proteins
that are resistant to digestion in the stomach - Genetically modify crops to decrease phytate
content - Reduces phytate content of corn and soybean meal
-
Phytate-P, of total P -
Normal Low phytate - Corn
75 35 - Soybeans
70 24 - Increases P bioavailability
-
P bioavailability, -
Normal Low phytate
23- Limitations of low phytate crops
- Low germination rates
- 4 23 reduction in seed weight
- Difficulties in separating grain hybrids
- Addition of vitamin D metabolites
- 1,25(OH)2 vitamin D increases P transport across
intestinal wall - Has additive effects with phytase
- Feeding 1,25 (OH)2 vitamin D and phytase can
replace .2 units or 50 of the inorganic P added
to chick diets - Limitation
- Excess vitamin D may be toxic
- Addition of probiotics
- Probiotics are microbial cultures dosed or fed to
establish a population of favorable bacteria - Feeding Lactobaccillus-based cultures increase P
retention by 22 in chickens
24- Balance diets closer to the P requirements
- Limit safety margins
- Swine industry commonly feeds P at 120 155 of
the NRC requirements - Swine diet
Manure P, lb/pig - .5 P
2.5 - .6 P
3.5 - Current actual requirements for poultry are 40
less than recommended by NRC - Phase feeding
- P requirement (as a of diet) decreases as
animals grow - Increasing number of phases to 4 or 5 or more
will reduce P excretion by 10 - Limitation
- Feeding and handling more diets
- Separate sex feeding
- P requirements for males gt P requirements for
females - Accurate real-time feed composition
- Book values are inaccurate
- Wet lab analysis of P and phytate-P is slow and
expensive - Near infrared reflectance spectroscopy (NIRS)
technology may help
25- Minimize feed variability
- Natural variability
- Processing
- Pelleting may reduce P bioavailability
- Proper weighing and mixing
- Minimize feed waste
- Each 1 increase in feed waste .04 lb/pig
increase of P in manure - Total potential for using available tools
(phytase, low phytate corn, phase feeding,
vitamin D) - Decreases P excretion by 40 to 60 in poultry
- Decreases P excretion by 50 to 60 in swine
26P DIGESTION AND METABOLISM IN RUMINANTS
- Rumen
Small intestine - Phytate-P
- Inorganic-P Undegraded
- Degraded
Very little
Feces -
(95-98 of - Inorganic P
excreted P) -
- Microbes
Passive Active -
absorption transport -
Circulating P
1,25(OH)2vitamin D -
kidney (Low Ca - Recycled to digestive Bone
or P) - tract via saliva
25(OH)vitamin D - (Supplies P to rumen Soft
tissue - microbes if diet is deficient
liver - 80 of total P excreted)
Excess
27FACTORS AFFECTING P ABSORPTION IN RUMINANTS
- Amounts of P consumed
- High P intake reduces P absorption
- CaP ratio
- Optimum is 21
- Excess amounts of Al, Fe, Mg, Mn, K, and fat
- Reduce P absorption by producing indigestible
complexes - Intestinal pH
- Lower intestinal pH increases P absorption
- P source
-
P availability, - Forages
64 - Energy and protein concentrates 70
- Mineral supplements
70 - Forage P concentration
- High soil P increases forage P concentration
- High forage P concentration reduces P absorption
- Forage maturity
- Forage P concentration decreases with maturity
- Forage fiber digestion decreases with maturity
decreasing P absorption
28STRATEGIES TO REDUCE PHOSPHORUS LOADING OF THE
ENVIRONMENT BY RUMINANTS
- Do not overfeed P
- Dairy
-
P in DM Manure P, lb/cow/lactation - Industry average
.52 64.9 - NRC requirement
.32-.42 42.2 - Adequate
.35 34.8 - Dry cow
.25 - - Reasons for excess feeding
- Belief that P supplementation will improve
reproductive performance - Studies show no improvement in reproduction above
.25 P - Aggressive marketing of P supplements
- Beef feedlot
- Steer (600-1200 lb)
Diet P, of DM - NRC requirement
0.20 0.30 - Adequate in experiments
0.14 0.16 - Reasons for excess feeding
- NRC requirement based on 1950 dairy cow data
- High grain diets contain 0.3 and require no
supplement
29- Beef cows
- Common P,
Physiological P reqt, - Season feed of DM
state of DM - Spring-summer Pasture 0.37-0.44
Lactating 0.22 - Fall Corn stalks 0.09
Early gestation 0.12 - Winter Grass-legume hay 0.26-0.34 Late
gestation 0.16 - Implications
- Phosphorus only need to be supplemented when
grazing or fed very mature grass forages or crop
residues - However, most producers supplement P year-round
- Reasons for excess P feeding
- Belief that continuous P supplementation is
needed for reproductive performance - Ease of supplementing minerals free choice to
provide safety margin - Results of feeding excess P
- Increases amount of P excreted
- Increases the solubility of the P excreted
- Amount of P lost in run-off increased 4 times if
dairy cow diets contain .5P vs. .4P
30- Difficulty in lowering P in ruminant diets
- High concentration of P in grains and grain
by-products - Grains contain adequate P (0.3) to meet
requirements of feedlot cattle without supplement - Grain by-products
- Contain high concentrations of P
-
P, DM - Wheat mids
1.02 - Distillers grains
0.90 - Corn gluten feed
1.00 - A large increase in ethanol plants will increase
the amounts of distillers grains available - 75 of distillers grains are fed to beef
cattle - A diet containing 40 distillers grains will
contain 0.55 P - If by-products are fed, more land will be needed
to apply at an agronomic rate - Strategic use of P reserves in cows
- Dairy cows may safely mobilize 500 to 1000 g P
from bone in early lactation - Could also be used for intervals in beef cows
- Ruminants effective at recycling P
- Mobilized P must be replaced at different times
of the year
31- Feeding ionophores
- Chemical feed additives that affect mineral
transport across membrane - Common ionophores
- Monensin (Rumensin)
- Lasalocid (Bovatec)
- Reduces P excretion
- Monitor feed status
- Analyse feeds
- Books values are inadequate
- Condition score cows
- Measure of cow fatness
- Scale (1 9)
- 1 very thin
- 5 desired
- 9 very fat
- If cows lt condition score 5, analyse diet for
energy, protein and minerals - P solubility in feces
- No soluble P means inadequate P in diet
32- Feed high quality forages
- Immature, high quality forages contain more P
that is more digestible than mature forages - Avoid excess calcium in diet
- Use improved grazing management practices
- Properly managed rotational grazing should limit
P loss in soil erosion from both upland and
riparian areas - Bale some pasture forage to remove P and to keep
the remainder of the pasture immature - Only fertilize pastures with P based on soil
analyses - Strategic supplementation to grazing cattle
- Only supplement if grazing mature forage on low P
soil - Limit use of free choice mineral
- In future, may be able to feed grains that are
genetically modified for a lower P content.
33POTENTIAL TO DECREASE P EXCRETION BY RUMINANTS
- Dairy
- 20 decrease in dietary P
- 25 30 decrease in manure P
- 50 decrease in P run-off from land
- Beef
- 33 decrease in dietary P
- 40 decrease in manure P (5.1 lb P/steer)
34MANURE HANDLING AND STORAGE TO MINIMIZE P LOADING
OF THE ENVIRONMENT
- Goals
- Maintain NP ratio
- Use strategies to minimize N loss
- Minimize P loss
- Minimize precipitation run-off
- P loss from lots and storage facilities is low if
run-off is minimized - Strategies
- Catch run-off from lots and storage areas
- Divert clean water from lots and storage areas
- Minimize the solubility of P in manure
- Gravity settling and mechanical separators will
remove 15 to 25 of the P in liquid manure - P decreases in the liquid fraction of manure in
lagoons and increases in the sludge - 65 of the P in manure will be in the sludge
- Addition of aluminum sulfate, magnesium chloride,
ferric chloride, and some Ca salts will
precipitate P from liquid manure in the solids
fraction - Enhance manure transport from farm
- Compost
35LAND APPLICATION STRATEGIES TO LIMIT P LOADING OF
THE ENVIRONMENT
- Goals
- Apply manure to meet crop P needs
- Apply manure to minimize risk of P transport to
water sources - Considerations
- Should manure be applied?
- Application rate?
36METHODS TO DETERMINE WHETHER MANURE P SHOULD BE
APPLIED
- Soil tests
- Measures available P relative to plant response
- If soil test is high or very high
- Manure should not be applied or applied only at
the agronomic rate depending on transport risk
determined by a P index - P index
- A measure of the risk of P transport to surface
water sources - Required for every field which manure applied on
it from a CAFO in Iowa - Integrates soil, landscape, and management
factors that influence P transport to surface
water sources - Identifies causes of P delivery and provides
options to decrease P transport
37- Considerations for the Iowa P index
- Erosion component
- Gross erosion (Slope, soil type, cover)
- Sediment trapping (Conservation practices)
- Sediment delivery (Amounts of sediment and
distance from stream) - Buffers
- Soil P test erosion (Sediment-bound P loss)
- Run-off component
- Run-off (Soil drainage)
- Precipitation (Annual)
- Soil P test run-off (Soluble P loss in run-off)
- P application (Total P fertilization)
- Subsurface drainage component
- Precipitation (Annual
- Flow factor (Presence of subsurface strata)
- Soil P test infiltration (Soluble P infiltrating
soil in drainage
38- Ranks risk of application site from 0 to 15
- Interpretation
- Very low (0 1)
- Effects of P losses from a field will be small
- Low (1 2)
- Current soil conservation and P management
practices do not pose threat - Medium (2 6)
- P delivery potential is low, but improved soil
conservation and P management practices should be
considered - High (6 - 15)
- Impacts of P on surface water is high. Improved
soil conservation and P management practices to
reduce P transport are required. - Very high (gt 15)
- Impacts of P on surface water is extreme.
Improved soil conservation and P management
practices to reduce P transport are required. - P management plan that may include
discontinuation of P application must be
implemented.
39CALCULATION OF MANURE APPLICATION RATE BASED ON
THE AGRONOMIC RATE FOR P
- Manure P production or concentration
- Manure_________
P2O5, lb/lb animal wt/yr - Swine Growing-finishing
0.13 - Sows litter
0.12 - Sows (gestation)
0.05 - Gilts
0.066 - Beef 450 750 lb
0.083 - Finishing
0.078 - Beef cows
0.10 - Dairy 50 lb milk/d
0.087 - 70 lb milk/d
0.096 - 100 lb milk/d
0.11 - Dry
0.074 - Heifers
0.033 - Poultry Layers
0.26 - Pullets
0.20 - Broilers
0.28 - Turkey
0.23
40- Availability of manure P to plants
- Affected by
- P retained during storage
- Type Proportion of excreted P
available to apply - Feedlot
.95 - Manure under roof
1.0 - Bedded swine
1.0 - Liquid/slurry
1.0 - Pit beneath slats
1.0 - Compost
.95 - Anerobic lagoon
.35 (Remainder in sludge) - P solubility in manure
- Greater in lagoon manure than solid or slurry
- Application method
- P retention greater from injection than surface
application - Soil
incorporation Broadcast Irrigation - -- of
manure P available after application--- - Scraped manure 80
70 - - Poultry house litter 80
70 -
41- P uptake by crop
- - Based on realistic yield expectations
-
P2O5 uptake and harvest - Corn
- Grain
0.36 lb/bu - Stover
9.16 lb/ton - Soybeans
0.88 lb/bu - Corn silage
4.01 lb/ton - Alfalfa hay
10.08 lb/ton - Alfalfa silage
7.56 lb/ton - Bromegrass hay
9.62 lb/ton
42- Calculation of manure application based on P
needs - Equations
- P2O5 needed, lb/ac RYE x P2O5 uptake and
harvest - Manure application, gal/ac P2O5 needed,
lb/ac/(Manure P2O5 conc x -
P
availability) - Example
- Field has a RYE for corn of 180 bu/acre
- Liquid manure containing 3.5 lb P2O5/1000 gal by
analysis is applied with irrigation - P2O5 needed, lb/ac 180 bu/ac x 0.36 lb P2O5/bu
64.8 lb/ac - Manure application, gal/ac 64.8 lb/ac /(3.5 lb
P2O5/1000 gal .80) -
23143 gal/ac - Manure application rate for P will be 25 to 50
of that for N - Manure application should usually be based on the
P rate - New EPA regulations will allow a single
application of manure to meet multiple year needs
for P on fields with - a low potential for run-off
- application does not exceed the N-based rate
during the first year -
43- Effects of using distillers grains for feeding
cattle on land base for manure application - Assumptions
- 2500 head feedlot with 2 groups per year
- Average weight, 975 lb
- lb P2O5/lb animal weight/year .078 (Corn based
diet) or .156 (Distillers grains diet) - Broadcast application 70 P availability
- ½ cropground available for land application
- Corn production, 200 bu/ac
- Corn P2O5 uptake .36 lb/bu
Corn, 1.9 miles
Distillers grains 2.7 miles