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EFFECT OF SEMI-EXTENSIVE PASTURE MANAGEMENT ON ITS BOTANICAL COMPOSITION AND ANIMAL PRODUCTION - M. Michalec, M. Zimková and O. Jezíková

Grassland and Mountain Agriculture Research Institute, Mládeznícka 36, 974 21 Banská Bystrica, Slovakia

SUMMARY

A grazing trial with heifers was conducted at Nemecká, Central Slovakia in 1986-89 (520 m; average annual rainfall 727 mm, during the growing season 424 mm; average annual temperature 6.3°C, during the growing season 13°C). The sward was semi-natural grassland, Poo-Trisetetum; fertilization: 120 kg N ha-1 + 35 kg P ha-1 annually.

Two systems of grazing were compared:

A. Heifers grazing on a young sward - the main grass species Poa pratensis, Lolium perenne, Festuca pratensis at the stage of tillering - in six paddocks with N-fertilization of 3 x 40 kg N ha-1.

B. Heifers grazing on an older sward - the dominant grass species (Poa pratensis) at flowering - in three paddocks with fertilization 2 x 60 kg N ha-1.

The different management and sward utilization (three or six paddocks) and the differently applied N-fertilization influenced the botanical composition and yield of the sward, liveweight gains (LWG) and meat production per ha. The main tendency in botanical composition of system A was: decrease of grass and herb species and increase of legumes; and of system B: amount of grass species stable, slow increase of legumes and decrease of herbs. The percentage of Trifolium repens reached a maximum of 24 percent (system A, 3rd grazing cycle in 1989).

Liveweight gains were 605 and 580 g head-1 day-1 for systems A and B, respectively. Corresponding stocking rates were 3.11 and 3.23 head ha-1 and average meat production, 448 and 433 kg ha-1.

Keywords: semi-extensive pasture management, botanical composition, grazing, liveweight gain, meat production

INTRODUCTION

Extensification is being called for in many European countries. This implies low inputs of fertilizers and semi-extensive systems of grazing. Within this scenario biodiversity in sward composition is likely and white clover has an important role to play in both its N-fixing and high nutritive value characteristics. This study aimed to quantify the botanical composition and meat production of semi-natural pasture under semi-extensive management.

MATERIALS AND METHODS

The grazing trial with heifers was conducted at Nemecká (Central Slovakia): 520 m; average annual rainfall 727 mm, during the growing season 424 mm; average annual temperature 6.3°C, during the growing season 13°C, in 1986-89. The sward was semi-natural grassland, Poo-Trisetum. The terrain was of northern exposure with 5-7°C declination.

Two systems of grazing were compared:

A. Grazing of heifers (Slovak Spot Breed) on a young sward - the main grass species (Poa pratensis, Lolium perenne, Festuca pratensis) at the stage of tillering - in six paddocks (å 1.58 ha) with 3 x 40 kg N ha-1 + 35 kg P ha-1 applied.

B. Grazing of heifers on the older sward - the dominant grass species at flowering stage - in three paddocks with 2 x 60 kg N + 35 kg P ha-1 applied.

Phosphorus fertilizer was applied each autumn and nitrogen after grazing the cycles (in system A after 1st, 2nd and 3rd cycles and in system B after 1st and 2nd cycles). For the A and B systems the grazed area was 1.58 and 1.72 ha, respectively; animals being in one paddock 3-7 and 6-15 days, respectively.

Botanical composition was evaluated by projective dominance (subjective method of species assessment in percentage).

RESULTS AND DISCUSSION

The botanical composition of the swards is shown in Tables 1 and 2.

The dominant grass species was Poa pratensis, its percentage in the 1st grazing cycle being 32-40 and 31-37 for A and B grazing systems, respectively. In the 3rd grazing cycle the percentage of Poa pratensis decreased from 1986 to 1989 by 8 and 17 in the A and B management systems, respectively.

Table 1. Botanical composition of swards in the 1st grazing cycle (%).


System A

System B

Years

1986

1987

1988

1989

1986

1987

1988

1989

Grasses

71

69

67

65

69

70

68

65

Legumes

7

9

12

15

8

9

12

13

Herbs

22

22

21

18

23

21

20

22

Bare spots

-

-

-

2

-

-

-

-

Dominant grass:









Poa pratensis

40

35

36

32

31

33

37

35

Dominant legume:









Trifolium repens

5

8

10

13

6

7

9

11

Dominant herb:









Taraxacum officinale

12

11

9

10

13

10

11

14

Table 2. The botanical composition of swards in the 3rd grazing cycle (%).


System A

System B

Years

1986

1987

1988

1989

1986

1987

1988

1989

Grasses

69

66

65

57

75

76

71

62

Legumes

15

16

22

27

10

15

17

20

Herbs

16

16

11

12

15

9

10

15

Bare spots

-

2

2

4

-

-

2

3

Dominant grass:









Poa pratensis

37

36

32

29

40

38

35

23

Dominant legume:









Trifolium repens

13

14

19

24

7

12

15

18

Dominant herb:









Taraxacum officinale

8

8

7

6

6

5

5

7

Both management systems maintained the development of white clover in the sward; maximum percentage was assessed in the 3rd grazing cycle: 13-24 and 7-18 in A and B systems, respectively. An increasing percentage of white clover in the sward was found from 1986 to 1989: maximum 24 percent in A system in 1989. The dominant herb species was Taraxacum officinale whose highest percentage was in the 1st grazing cycle: 9-12 and 10-14 in A and B management systems, respectively.

Nösberger (1994) and Bakker (1994) have described the benefits of biodiversity potential from extensification methods, though extreme extensification is not the aim of production systems. Periodic oscillations in white clover content have been suggested as an indication that the sward-management-grazing animal complex is working well (Schwinning and Parsons, 1996).

The potential of semi-extensive pasture management depends also on stocking rate (Table 3). The higher stocking rate was in system B though there were differences between years; the lowest stocking rate was assessed in 1988 which was caused by lower forage production due to dry weather. The effect of semi-extensive pasture management on LWG was not as significant as expected (Table 4) but significant differences were found between years. The lowest daily LWG was in 1988: 520 and 490 g head-1 day-1 for systems A and B, respectively.

Table 3. Average stocking rate (heifers ha-1) in 1986-89.


Stocking rate

Years

System A

System B

1986

2.60

3.30

1987

3.27

3.22

1988

2.82

2.74

1989

3.73

3.67

mean

3.11

3.23

Table 4. Average daily LWG of heifers (g head-1 d-1).


Years

Systems

1986

1987

1988

1988

Mean

A

620

630

520

650

605

B

640

600

490

590

580


LSD at P < 0.05

for grazing systems

27.15


for years

18.42

LSD at P < 0.01

for grazing systems

41.39


for years

27.98

Table 5. Meat production (kg ha-1)


Meat production

Years

System A

System B

1986

385

429

1987

447

395

1988

335

285

1989

624

622

Mean

448

433

There were differences in beef production between the years, the lowest meat production being in 1988 and averages were 448 and 433 kg ha-1 for systems A and B, respectively (Table 5). Good results of daily liveweight gains and beef production from grass/clover swards have also been demonstrated by Davies and Hopkins (1996).

REFERENCES

Bakker, J.P. 1994. Nature management in Dutch grasslands. Grassland Management and Nature Conservation. Occasional Symposium No 28. British Grassland Society, 115-124.

Davies, D.A. & Hopkins, A. 1996. Production benefits of legumes in grassland. In: Younie, D. (Ed.). Legumes in Sustainable Farming Systems. Occasional Symposium No 30. British Grassland Society, 234-246.

Nösberg et al. 1994. Grassland production system and nature conservation. Grassland and Society. Proceedings of the 15th General Meeting of the European Grassland Federation, 255-265.

Schwinning, S. & Parsons, A.J. 1996. Interaction between grasses and legumes: understanding variability in species composition. In: Younie, D. (Ed). Legumes in Sustainable Farming Systems. Occasional Symposium No 30. British Grassland Society, 153-163.


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