Biologically adjusted P cycle as a measure to reduce P losses, an example for Finnish agriculture

Biologically adjusted P cycle as a measure to reduce P losses, an example for Finnish agriculture Eila Turtola (1), Riitta Lemola (1), Jouni Nousiaine...
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Biologically adjusted P cycle as a measure to reduce P losses, an example for Finnish agriculture Eila Turtola (1), Riitta Lemola (1), Jouni Nousiainen (2), Pekka Huhtanen (3), Risto Uusitalo (1) and Elena Valkama (1) (1) MTT, Plant Production Research (2) MTT, Biotechnology and Food Research (3) SLU, Agricultural Research for Nothern Sweden

COST 869, Wageningen, May 19, 2009

Starting -1points:

Specialization in livestock and plant production

t P a-1

tNa

100000

320000

P fertilisation is obviously the most 240000 important background factor for DRP (bioavailable PP) losses from fields to waters 160000

High chemical fertilizer inputs

80000 60000 40000 20000

P fertilisation rates in Deposition Finland were high starting from theNbeginning of fixation 1960s. Manure Fertilization Output

Fertilisation has been reduced considerably in the last 15-20 years.

Deposition Weathering Manure Fertilization Output

Antikainen et al. 2005

2000

1990

1980

1970

1960

1950

1940

1930

1920

1910

2000

1990

0

1980

1970

1960

1950

1940

1930

1920

1910

In80000 modern agriculture, inputs of commercial fertilizers have been large0

(Sweden +2, Norway +13, Denmark +11, Netherlands+16, Hungary -15 kg/ha) .

Karjanlanta Manure

Sato Yield

Tase Bal

30 25 20 15 10 5

2007

2005

2003

2001

1999

1997

1995

1993

1991

1989

0 1987

The average P balance was +30 kg/ha in the end of 1980s, but is now +6 kg/ha

Ostolann. Chemic

1985

P inputs in manure and outputs in yield have remained stationary

35

Fosfori, kg/ha Phosphorus, kg/ha

From the highest levels in late 1980s (28 kg/ha) the chemical fertilizer inputs of P have decreased down to 8 kg/ha

Whole Finland

12 10 8 6 4 2 2001-2005

1996-2000

1991-1995

1986-1990

1981-1985

1976-1980

1971-1975

1966-1970

1961-1965

0

South-Western Finland

20 18 16 14 12 10 8 6 4

Uusitalo et al. 2007

2001-2005

1996-2000

1991-1995

1986-1990

1981-1985

1976-1980

1971-1975

1966-1970

2 0 1961-1965

Consequently, national monitoring studies have found only small or no decrease in P concentrations on agriculturally loaded rivers

14

1955-1960

Due to still positive balances, soil test P has not decreased considerably during the last 15-20 years, or has remained stationary (’good’) in regions with intensive animal production as in SouthWestern Finland

Soil test P, mg/l P-luku, mg/l

The average soil test P (PAc) was raised from 5 mg/l (’moderate’) to 12-14 mg/l (’satisfactory’) by the surplus P balances of 20-30 kg/ha

mg/l SoilMaan testP-luku, P, mg/l

16

P fertilisation and P balance on Finnish dairy farms 45

Still, livestock farms use commercial fertilizers. E.g. in dairy farms, fertilizer P seems to raise directly the P balances

40 35

P-balance (kg/ha)

Manure P is produced and used mostly in regions of concentrated livestock production

30 y = 1.078x + 1.56 R2 = 0.854

25 20 15 10 5 0 0

5

10

15

20

25

30

35

P-fertizer (kg/ha)

Since crop yields, at least in the national and regional levels, have not been affected by the recent, lower P fertilisation, is there further potential for reduction?

Tuori et al.

40

Moreover, there may be potential to adjust animal feeding in terms of P, and reach lower P contents in manure Manure-P, kg/ha

Manure-P, fur animals kg/ha 0 0,01-0,49 0,5-1,9 2,0-4,9 5,0-9,9 10-20 20-50 50-100

Maps: Kaarina Grek and Harri Lilja MTT

We set 2 questions: >> How large is the potential for adjusting P use further in Finnish agriculture (feeding of livestock and fertilisation of agricultural crops) without lowering the production? >> How large is the related potential for reduction of DRP losses to surface waters?

Step 1: Comparison of current P feeding of animals to that justified by biological responses according to feeding trials, i.e. avoiding overuse ● The current P content of manure (year 2005) was estimated Renewal

●New, lower P content of manures (for cow, pig, poultry and fur animals) were then calculated with biological response functions, taking into account economic effects (no negative effects on the net income, Huhtanen et al.)

Feed import

Commercial fertilizers Sold plant products

Storage and feeding

Plant production

Nutrient balances

Milk production

Manure storage

Nutrient losses

Pekka Huhtanen SLU

Sold animals

Sold milk & animals

Bying Selling

Result (1): Adjustment of P feeding would result in 12% lower P content in manure

Area

Current manure-P Adjusted manure-P mill.kg/year mill.kg/year

Whole Finland Uusimaa Varsinais-Suomi Pohjanmaa

16,5 0,48 1,9 2,9

Jouni Nousiainen MTT, Pekka Huhtanen SLU

14,5 0,43 1,7 2,6

Step 2: Comparison of current P use in plant production to that justified by biological responses according to fertilisation trials, i.e. avoiding overuse ● The crop responses to soil test P and P fertilisation were considered, but economy was not taken into account

● Need of P fertilisation was estimated according to amounts giving maximum yields (Valkama et al. 2009)

30

"Low"

"Medium and high"

Yield increase (%)

25 20 (28)

15 10 5 0 -5

(12)

(48) (21)

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