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Philip Moore
USDA/ARS
Poultry Production and Product Safety Research Unit
Fayetteville, Arkansas
Development of a New Manure Amendment
for Reducing Ammonia Volatilization and
Phosphorus Runoff from Poultry Litter
• Phosphorus is generally the limiting nutrient for eutrophication, at
least in freshwater systems.
• The majority (90% ) of P in runoff from pastures and no-till land
that has been fertilized with animal manure is dissolved reactive P,
which is the form most available for algal uptake.
• In the early 1990’s, we found that Al, Ca, or Fe amendments could
be used to reduce water soluble P in poultry litter and we
hypothesized that this would result in reduced P runoff (Moore and
Miller, 1994).
• In subsequent research using rainfall simulators, we found alum
additions to poultry litter reduced P runoff by 87% from small plots
(Shreve et al., 1995).
Phosphorus runoff from poultry litter
Alum also reduces heavy metal and estrogen runoff
•Nichols et al. (1997) found
that estrogen levels in runoff
from alum-treated litter were
42% lower than normal litter.
•Moore et al. (1998) found that
As, Cu, Zn levels in runoff
water from alum-treated litter
were 40-50% lower than
normal litter and Al runoff was
not affected. Normal Litter Alum-treated Litter
• In the runoff study conducted by Shreve et al. (1995), we found
fescue yields were higher with alum-treated litter, due to increased
N uptake and hypothesized this was due to less NH3 volatilization.
• High NH3levels in poultry houses cause poor weight gains, poor
feed conversion, lower egg production, increased susceptibility to
disease, and blindness in birds. Atmospheric NH3 contamination
can lead to environmental problems, such as PM-10s, excessive N
loading into aquatic environments and soil acidification.
• In a series of lab studies, alum was found to greatly reduce NH3
losses from litter and was more cost-effective than other products
we tested (Moore et al., 1996).
• In an EPA 319 demonstration conducted on two broiler farms, NH3
emissions were reduced by 70% in commercial broiler houses
Alum reduces ammonia emissions from manure
Reducing ammonia loss and P runoff with alum
• Alum is added between
flocks to the litter. It
provides protons, which
shifts the NH3/NH4
+
equilibria toward NH4
+
.
• Lower litter pH also reduces
pathogens (Campylobacter
and Salmonella) in litter
(Lines, 2002).
• Aluminum in alum reacts
with P to make an insoluble
aluminum phosphate
mineral, which results in
NH3 + H+
---> NH4
+
ammonia ammonium
• Alum additions resulted in heavier birds, improved feed
conversion, and lower condemnation, which is probably due to
lower in-house NH3 levels and fewer pathogens in the litter (Moore
et al., 1999, 2000).
• Alum use also lowered the ventilation requirements in broiler
houses, particularly in winter, which resulted in lower propane and
electricity use (Moore et al., 2000; Worley et al., 1999).
• Recent studies have shown alum also lowers CO2 emissions, but
does not affect N2O or CH4 emissions (Eugene et al., 2015).
• Higher N content in litter results in higher crop yields with alum
(Shreve et al., 1995; Moore and Edwards, 2005).
Economic benefits of alum
Alum use by the poultry industry
• We patented this technology in 1997
and it was licensed to General
Chemical, which markets poultry
grade alum as “Al+
Clear”.
• Alum use by the poultry industry has
increased dramatically during the
past decade.
• Because of the economic benefits of
this BMP over one billion chickens
are grown each year with alum.
• The USDA/NRCS developed a Conservation Practice Standard for
litter amendments like alum, hence, EQIP cost-sharing is now
available for this practice.
• Likewise, many of the biggest poultry companies in the U.S.
provide cost-share for growers who use alum.
• There are approximately 9 billion broilers raised annually in the
U.S., yet only 1 billion are grown with alum.
• The question is, if alum has so many benefits, why doesn’t
everyone use it? The reason is simple ($).
Acceptance of alum as a BMP
• The price of alum has increased significantly in the past 20 years
and cost-sharing from NRCS or the integrator is not always
available. Plus the economic benefits (particularly better feed
conversion) helps the integrator a lot more than the grower.
• When we did the original alum work in the 1990s we spent a lot
of time trying to find a cheaper “waste” product to use to
precipitate P and reduce ammonia loss, but none were suitable.
• We tested red mud and brown mud, which are waste streams
from aluminum mining that are left over from the Bayer process,
which uses sodium hydroxide to extract aluminum from bauxite.
They had little effect on soluble P and were buffered at a high
pH, which would increase ammonia loss.
• Other wastes streams tested were loaded with toxic metals.
Why not use an industrial waste stream?
Alum mud
• There is another method that is used to make alum. In this second
method, bauxite is reacted with sulfuric acid for a long period in a
big reactor. The solids are then allowed to settle and the liquid on
top, which is liquid alum, is either sold or dried to make dry alum.
• The solids that settle out are referred to as “alum mud”, which is a
waste material. It is landfilled at a cost of about $30/wet ton.
• Alum mud is acidic because it has been reacted with sulfuric acid,
plus it has a very high aluminum content. However it is not
acidic enough alone to be a litter amendment. When acid is
added to it, the mixture becomes wet and very sticky and difficult
to handle.
• Experiments were conducted on different mixtures using the
Mixture alum mud bauxite sulfuric acid liquid alum Water
1 200 15 135 0 0
2 185 30 140 0 0
3 170 45 145 0 0
4 215 0 130 0 0
5 185 15 125 30 0
6 0 215 195 0 0
7 110 105 160 0 0
8 155 45 135 30 0
9 0 200 180 30 0
10 175 0 95 90 0
11 140 0 75 150 0
12 145 30 100 95 0
13 0 0 7.5 74.7 17.9
14 115 0 50 210 0
15 140 60 135 35 0
Amounts of various components (grams) in different mixtures from “Quick & Dirty Studies”
Quick & Dirty Results
• Almost all of our mixtures resulted in exothermic reactions.
Sometimes they were a bit violent. Most mixtures would harden
within 4-5 minutes of adding sulfuric acid.
• Some mixtures became as hard as granite. Although they are
unsuitable as a litter amendment, we are going to try to patent
these as a new construction material (replacement for concrete).
Other mixtures resulted in a product that was similar to wet sticky
mud, which would also be unsuitable for processing & handling.
• When just a little bit of bauxite (5-15%) is mixed with the right
amount of alum mud (45-60%), then treated with sulfuric acid
(35-50%), it results in a nice, dry, crumbly product that can be
handled, bagged and easily spread in chicken houses.
Laboratory Ammonia Volatilization Study
• 100 g fresh poultry litter was placed into 44 plastic containers.
There were 11 treatments with 4 reps/treatment in RBD.
• Treatments were surface applied to litter without mixing. Most
amendment rates were 4 g/100 g litter (~100 lbs/1,000 ft2
). This
is a low rate, but it is typical of what is used by the industry.
• Ammonia-free air passed through containers and any ammonia
exiting was trapped in boric acid traps which were titrated daily.
• At day 14, litter was analyzed for pH, EC, soluble metals, soluble
P, and KCl-extractable ammonium.
Treatments
Control
4 g dry alum
8 g liquid alum (sprayed on with mister)
4 g of mixture 1 (57.1 % alum mud, 4.3% bauxite, 38.6% sulfuric acid)
4 g of mixture 2 (52.1 % alum mud, 8.5% bauxite, 39.4% sulfuric acid)
4 g of mixture 3 (47.2% alum mud, 12.5% bauxite, 40.3% sulfuric acid)
4 g of mixture 5 (52.1% alum mud, 4.2% bauxite, 35.2 % sulfuric acid, 8.5% liquid alum)
4 g of mixture 6 (52.4% bauxite, 47.6% sulfuric acid)
4 g of mixture 10 (48.6% alum mud, 26.4% sulfuric acid, 25% liquid alum)
4 g of mixture 12 (39.2% alum mud, 8.1% bauxite, 27% sulfuric acid, 25.7% liquid alum)
8 g of mixture 13 (9.1% sulfuric acid, 90.9% liquid alum, sprayed on with mister)
LSD = 442
LSD = 442
Treatment Litter pH
in water
Cumulative
NH3 Loss
in 14 days
(mg N/kg)
KCl
Extractable
NH4
(mg N/kg)
Water
Extractable
P
(mg P/kg)
Water
Extractable
Zn
(mg Zn/kg)
Control 8.89 a 3109 a 3300 e 1234 a 55.0 a
Dry Alum 7.97 c 440 c 5660 abcd 920 b 36.3 def
Liquid Alum 8.12 bc 782 bc 5620 bcd 656 e 34.5 ef
Mixture 1 8.13 bc 855 bc 6050 ab 862 bc 38.0 bcd
Mixture 2 8.20 bc 1016 b 6080 a 907 bc 40.5 b
Mixture 3 8.24 b 850 bc 5840 abc 735 de 37.3 cde
Mixture 5 8.19 bc 955 b 5920 abc 872 bc 38.8 bcd
Mixture 6 8.16 bc 802 bc 5980 ab 850 bc 38.6 bcd
Mixture 10 8.17 bc 1167 b 5320 d 934 b 39.3 bc
Mixture 12 8.26 bc 1032 b 5490 cd 816 cd 38.8 bcd
Mixture 13 8.05 bc 971 b 5770 abc 707 e 34.0 f
LSD 0.05 0.25 442 445 99.9 2.85
Conclusions
• All of the manure amendments resulted in significantly lower
ammonia volatilization than the control (untreated litter).
• Ammonia volatilization was reduced by 62 to 73% with the 8
new manure amendments, which were not significantly different
from liquid alum. Three were not different from dry alum.
• All of the amendments reduced water extractable P (WEP). Three
of the new mixtures resulted in lower WEP than dry alum.
• The most promising products were mixtures of alum mud, bauxite
and sulfuric acid.
• The potential impact of these new products could be enormous
since they could be produced for less than half the price of alum.
Future Research
• Feeding trials will soon be conducted where the diets of broilers
will be laced with various amounts of the alum mud litter
amendment. We did this same study with alum before treating
litter in commercial houses to make sure that litter consumption
by chickens didn’t result in high aluminum contents of meat.
• Pen trials will then be conducted to compare ammonia emissions
and water extractable P in litter treated with alum versus the new
alum mud amendment. Bird performance will also be evaluated.
• Assuming no problems are encountered in the feeding or pen trial
described above, then this product will be evaluated in
commercial broiler houses.

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Development of a New Manure Amendment for Reducing Ammonia Volatilization and Phosphorus Runoff from Poultry Litter

  • 1. Philip Moore USDA/ARS Poultry Production and Product Safety Research Unit Fayetteville, Arkansas Development of a New Manure Amendment for Reducing Ammonia Volatilization and Phosphorus Runoff from Poultry Litter
  • 2. • Phosphorus is generally the limiting nutrient for eutrophication, at least in freshwater systems. • The majority (90% ) of P in runoff from pastures and no-till land that has been fertilized with animal manure is dissolved reactive P, which is the form most available for algal uptake. • In the early 1990’s, we found that Al, Ca, or Fe amendments could be used to reduce water soluble P in poultry litter and we hypothesized that this would result in reduced P runoff (Moore and Miller, 1994). • In subsequent research using rainfall simulators, we found alum additions to poultry litter reduced P runoff by 87% from small plots (Shreve et al., 1995). Phosphorus runoff from poultry litter
  • 3. Alum also reduces heavy metal and estrogen runoff •Nichols et al. (1997) found that estrogen levels in runoff from alum-treated litter were 42% lower than normal litter. •Moore et al. (1998) found that As, Cu, Zn levels in runoff water from alum-treated litter were 40-50% lower than normal litter and Al runoff was not affected. Normal Litter Alum-treated Litter
  • 4. • In the runoff study conducted by Shreve et al. (1995), we found fescue yields were higher with alum-treated litter, due to increased N uptake and hypothesized this was due to less NH3 volatilization. • High NH3levels in poultry houses cause poor weight gains, poor feed conversion, lower egg production, increased susceptibility to disease, and blindness in birds. Atmospheric NH3 contamination can lead to environmental problems, such as PM-10s, excessive N loading into aquatic environments and soil acidification. • In a series of lab studies, alum was found to greatly reduce NH3 losses from litter and was more cost-effective than other products we tested (Moore et al., 1996). • In an EPA 319 demonstration conducted on two broiler farms, NH3 emissions were reduced by 70% in commercial broiler houses Alum reduces ammonia emissions from manure
  • 5. Reducing ammonia loss and P runoff with alum • Alum is added between flocks to the litter. It provides protons, which shifts the NH3/NH4 + equilibria toward NH4 + . • Lower litter pH also reduces pathogens (Campylobacter and Salmonella) in litter (Lines, 2002). • Aluminum in alum reacts with P to make an insoluble aluminum phosphate mineral, which results in NH3 + H+ ---> NH4 + ammonia ammonium
  • 6. • Alum additions resulted in heavier birds, improved feed conversion, and lower condemnation, which is probably due to lower in-house NH3 levels and fewer pathogens in the litter (Moore et al., 1999, 2000). • Alum use also lowered the ventilation requirements in broiler houses, particularly in winter, which resulted in lower propane and electricity use (Moore et al., 2000; Worley et al., 1999). • Recent studies have shown alum also lowers CO2 emissions, but does not affect N2O or CH4 emissions (Eugene et al., 2015). • Higher N content in litter results in higher crop yields with alum (Shreve et al., 1995; Moore and Edwards, 2005). Economic benefits of alum
  • 7. Alum use by the poultry industry • We patented this technology in 1997 and it was licensed to General Chemical, which markets poultry grade alum as “Al+ Clear”. • Alum use by the poultry industry has increased dramatically during the past decade. • Because of the economic benefits of this BMP over one billion chickens are grown each year with alum.
  • 8. • The USDA/NRCS developed a Conservation Practice Standard for litter amendments like alum, hence, EQIP cost-sharing is now available for this practice. • Likewise, many of the biggest poultry companies in the U.S. provide cost-share for growers who use alum. • There are approximately 9 billion broilers raised annually in the U.S., yet only 1 billion are grown with alum. • The question is, if alum has so many benefits, why doesn’t everyone use it? The reason is simple ($). Acceptance of alum as a BMP
  • 9. • The price of alum has increased significantly in the past 20 years and cost-sharing from NRCS or the integrator is not always available. Plus the economic benefits (particularly better feed conversion) helps the integrator a lot more than the grower. • When we did the original alum work in the 1990s we spent a lot of time trying to find a cheaper “waste” product to use to precipitate P and reduce ammonia loss, but none were suitable. • We tested red mud and brown mud, which are waste streams from aluminum mining that are left over from the Bayer process, which uses sodium hydroxide to extract aluminum from bauxite. They had little effect on soluble P and were buffered at a high pH, which would increase ammonia loss. • Other wastes streams tested were loaded with toxic metals. Why not use an industrial waste stream?
  • 10. Alum mud • There is another method that is used to make alum. In this second method, bauxite is reacted with sulfuric acid for a long period in a big reactor. The solids are then allowed to settle and the liquid on top, which is liquid alum, is either sold or dried to make dry alum. • The solids that settle out are referred to as “alum mud”, which is a waste material. It is landfilled at a cost of about $30/wet ton. • Alum mud is acidic because it has been reacted with sulfuric acid, plus it has a very high aluminum content. However it is not acidic enough alone to be a litter amendment. When acid is added to it, the mixture becomes wet and very sticky and difficult to handle. • Experiments were conducted on different mixtures using the
  • 11. Mixture alum mud bauxite sulfuric acid liquid alum Water 1 200 15 135 0 0 2 185 30 140 0 0 3 170 45 145 0 0 4 215 0 130 0 0 5 185 15 125 30 0 6 0 215 195 0 0 7 110 105 160 0 0 8 155 45 135 30 0 9 0 200 180 30 0 10 175 0 95 90 0 11 140 0 75 150 0 12 145 30 100 95 0 13 0 0 7.5 74.7 17.9 14 115 0 50 210 0 15 140 60 135 35 0 Amounts of various components (grams) in different mixtures from “Quick & Dirty Studies”
  • 12. Quick & Dirty Results • Almost all of our mixtures resulted in exothermic reactions. Sometimes they were a bit violent. Most mixtures would harden within 4-5 minutes of adding sulfuric acid. • Some mixtures became as hard as granite. Although they are unsuitable as a litter amendment, we are going to try to patent these as a new construction material (replacement for concrete). Other mixtures resulted in a product that was similar to wet sticky mud, which would also be unsuitable for processing & handling. • When just a little bit of bauxite (5-15%) is mixed with the right amount of alum mud (45-60%), then treated with sulfuric acid (35-50%), it results in a nice, dry, crumbly product that can be handled, bagged and easily spread in chicken houses.
  • 13. Laboratory Ammonia Volatilization Study • 100 g fresh poultry litter was placed into 44 plastic containers. There were 11 treatments with 4 reps/treatment in RBD. • Treatments were surface applied to litter without mixing. Most amendment rates were 4 g/100 g litter (~100 lbs/1,000 ft2 ). This is a low rate, but it is typical of what is used by the industry. • Ammonia-free air passed through containers and any ammonia exiting was trapped in boric acid traps which were titrated daily. • At day 14, litter was analyzed for pH, EC, soluble metals, soluble P, and KCl-extractable ammonium.
  • 14. Treatments Control 4 g dry alum 8 g liquid alum (sprayed on with mister) 4 g of mixture 1 (57.1 % alum mud, 4.3% bauxite, 38.6% sulfuric acid) 4 g of mixture 2 (52.1 % alum mud, 8.5% bauxite, 39.4% sulfuric acid) 4 g of mixture 3 (47.2% alum mud, 12.5% bauxite, 40.3% sulfuric acid) 4 g of mixture 5 (52.1% alum mud, 4.2% bauxite, 35.2 % sulfuric acid, 8.5% liquid alum) 4 g of mixture 6 (52.4% bauxite, 47.6% sulfuric acid) 4 g of mixture 10 (48.6% alum mud, 26.4% sulfuric acid, 25% liquid alum) 4 g of mixture 12 (39.2% alum mud, 8.1% bauxite, 27% sulfuric acid, 25.7% liquid alum) 8 g of mixture 13 (9.1% sulfuric acid, 90.9% liquid alum, sprayed on with mister)
  • 15.
  • 16.
  • 19. Treatment Litter pH in water Cumulative NH3 Loss in 14 days (mg N/kg) KCl Extractable NH4 (mg N/kg) Water Extractable P (mg P/kg) Water Extractable Zn (mg Zn/kg) Control 8.89 a 3109 a 3300 e 1234 a 55.0 a Dry Alum 7.97 c 440 c 5660 abcd 920 b 36.3 def Liquid Alum 8.12 bc 782 bc 5620 bcd 656 e 34.5 ef Mixture 1 8.13 bc 855 bc 6050 ab 862 bc 38.0 bcd Mixture 2 8.20 bc 1016 b 6080 a 907 bc 40.5 b Mixture 3 8.24 b 850 bc 5840 abc 735 de 37.3 cde Mixture 5 8.19 bc 955 b 5920 abc 872 bc 38.8 bcd Mixture 6 8.16 bc 802 bc 5980 ab 850 bc 38.6 bcd Mixture 10 8.17 bc 1167 b 5320 d 934 b 39.3 bc Mixture 12 8.26 bc 1032 b 5490 cd 816 cd 38.8 bcd Mixture 13 8.05 bc 971 b 5770 abc 707 e 34.0 f LSD 0.05 0.25 442 445 99.9 2.85
  • 20. Conclusions • All of the manure amendments resulted in significantly lower ammonia volatilization than the control (untreated litter). • Ammonia volatilization was reduced by 62 to 73% with the 8 new manure amendments, which were not significantly different from liquid alum. Three were not different from dry alum. • All of the amendments reduced water extractable P (WEP). Three of the new mixtures resulted in lower WEP than dry alum. • The most promising products were mixtures of alum mud, bauxite and sulfuric acid. • The potential impact of these new products could be enormous since they could be produced for less than half the price of alum.
  • 21. Future Research • Feeding trials will soon be conducted where the diets of broilers will be laced with various amounts of the alum mud litter amendment. We did this same study with alum before treating litter in commercial houses to make sure that litter consumption by chickens didn’t result in high aluminum contents of meat. • Pen trials will then be conducted to compare ammonia emissions and water extractable P in litter treated with alum versus the new alum mud amendment. Bird performance will also be evaluated. • Assuming no problems are encountered in the feeding or pen trial described above, then this product will be evaluated in commercial broiler houses.