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Variability in early growth and biomass accumulation in a progeny trial of Prosopis alba - L.N. Harsh, J.C. Tewari, N.K. Sharma and M.D. Bohra


Central Arid Zone Research Institute, Jodhpur 342003, India

Introduction

The vegetation of the hot desert region of India, classified as dry tropical thorn forests (Champion and Seth, 1968), is experiencing a high biotic pressure due to ever increasing human and livestock population (densities of 64 and 113 individuals/km2 respectively). As a consequence of this, the forest cover has been reduced to only 1% of the total land surface area of the region, with the remainder highly degraded forms (Tewari et al., 1993). Furthermore, hostile environmental conditions do not support the regeneration of natural vegetation. The desert landscape of western Rajasthan, known as the Thar desert, accounts for more than 61% of the total area of Indian hot arid regions. According to a recent estimate, the fuelwood requirement at present is more than 520,000 t and the projected requirement for 2001 is around 680,000 t, whereas availability of fuelwood at present is only 70,000 t (Anonymous, 1987). To bridge this gap between demand and supply of woody biomass, it is essential to raise large scale plantations of fast growing multi-purpose tree species (MPTS) in this desert tract (Mann and Muthana, 1984). Various species of the genus Prosopis are found to be very adaptable to the environmental conditions encountered in this hot arid region of India (Mann and Saxena, 1982). The present investigation was carried out on a progeny trial of 30 accessions of P. alba, to test their acclimatisation, adaptability and genetic variability; and also to assess the possibility of selection of plus trees for future plantation programmes in the arid environmental conditions of India.

Materials and methods

The experiment was conducted at the silvaetum of the Central Arid Zone Research Institute, Jodhpur (26o18’N, 73o08’E). The climate is typically arid, characterised by exceptionally hot dry summers, sub-humid monsoons and cold dry winters, with climatic details recorded at the experimental site during the period of study presented in Table 1. The soil is a sandy loam (Camborthid) with a pH of 8.1 and has low nutrient levels, with 0.23% organic carbon, 0.03% nitrogen and 0.02% phosphorus (Dhir, 1984). Thirty accessions of P. alba, obtained from Texas A&M University, Kingsville, U.S.A. were used in the this investigation. All were of Argentinean origin, from Cordoba, Salta and

Table 1. Mean monthly rainfall and temperatures recorded at the experimental site during the entire period of experimentation.


Rainfall (mm)

Max. temp. (oC)

Max. temp. (oC)

January

13

26

11

February

4

28

12

March

2

34

18

April

17

38

23

May

3

43

27

June

29

42

28

July

122

37

26

August

116

33

27

September

87

34

23

October

4

37

19

November

2

32

15

December

0

28

11

Catamarca, from areas receiving 250-700 mm rainfall per year. The term accession is used here to describe seeds from single tree representative of one location. Seeds were scarified with concentrated sulphuric acid for 15 minutes and sown into polythene bags (25 x 10 cm) containing a 1:2:1 ratio of manure, sand and clay in February 1991. Five month old seedlings were then out-planted in July, at a spacing of 2.5 x 4.0 m in a randomised complete block design with four replications, each having five plants. Plants were watered fortnightly in the summer and once a month during the winter (15 l/plant), and manual weeding was carried out twice, in the first year after planting.

Data for survival, plant height and collar diameter of all accessions were recorded at 6, 18 and 30 months, at the end of each growing season. At 30 months, the above ground biomass was also estimated using diameter at 15 cm above ground level on single stemmed and multi-stemmed trees. With multi-stemmed trees, the diameters of different stems (up to a maximum of 5 stems/plant) were measured, and the biomass of each stem was estimated before being pooled to obtain the total above ground biomass of the plant. The following empirical equation developed by Felker et al., (1989) for P. alba was used for the estimation of biomass in both single stemmed and multi-stemmed trees:

log10 dry weight (kg) =

2.1905 {log10 stem diameter (cm)} - 0.9811.

Replication means of registered data were used for statistical analysis using the computer software “SPAR” (Doshi and Gupta, 1991).

Results and discussion

Treatment means were found to be significant for plant height and estimated biomass but not for collar diameter (Table 2). Of the 30 accessions of P. alba, only a few consistently showed improved performance. Acc. no. 65 was found to be consistently better performing in terms of plant height, collar diameter and biomass, height being 60 cm, 102 cm and 225 cm, while the collar diameter was 1.06 cm, 1.76 cm and 4.19 cm, over the 3 growing periods. The estimated biomass was 7.05 kg/tree after 30 months. This accession was never in first place in the rank order for any character but performed better than average for all three characters and maintained good growth throughout the trial.

Acc. no. 67 performed relatively poorly in the first two growing periods but by 30 months it had attained a height of 259 cm and was placed first in the overall ranking, with increments in collar diameter also following a similar trend. The low order of estimated biomass (2.39 kg/tree) for this accession may perhaps be due to a lower number of stems per plant. Acc. nos. 28, 65, 73, 78, 120, 147 and 151 performed poorly for plant height after 6 months but later grew considerably. Acc. nos. 28, 78, 120, 147 and 151 showed relatively better growth in terms of collar diameter. Acc. no. 78 had a collar diameter of only 0.97 cm after 6 months, but performed very well later and registered maximum collar diameter (4.36 cm) thus acquiring first place in the ranking after 30 months. Acc. nos. 67 and 73 exhibited poor performance in the first two growing periods but after 30 months they had achieved 2nd and 3rd ranks respectively. Maximum estimated biomass (7.84 kg/tree) was recorded for acc. no. 146, followed by acc. no. 65 (7.05 kg/tree). However, the performance of acc. no. 146 was relatively poor in terms of plant height and collar diameter, the high biomass production in this accession perhaps due to its vigorous multi-stemmed form.

Concerning genetic parameters, the magnitude of PCV was more than GCV in all the three growing periods for both plant height and collar diameter, and also for biomass after 30 months, indicating interactions of some environmental factors (Table 3). In general, PCV showed an increasing trend with age for both plant height and collar diameter. For plant height, the magnitude of GCV was similar throughout the trial, but for collar diameter it was at a maximum (10.79%) after 18 months and minimum (5.68%) after 6 months. Heritability estimates in general showed a decreasing trend with age for both the characters.

For plant height, results after 6 months appeared most suitable for effective selection as maximum heritability as well as genetic advance as a percentage of the mean were recorded at this stage (Table 3). In the case of collar diameter, results after 18 months appeared to be more suitable, also true if simultaneous selection is practised, for both plant height and collar diameter. At this stage, GCV and heritability were relatively higher for both traits, which is further substantiated by the value of genetic advance as a percentage of the mean. The biomass GCV, heritability and genetic advance as a percentage of the mean were 26.07%, 20.10% and 23.96% respectively. Genetic parameters computed in the present investigation indicated that through simple selection, more gain is possible in biomass production than for plant height and collar diameter. Such changes in genetic parameters with age (from juvenile to mature stages) have also been reported with P. pallida (Sharma et al., 1993), Liquidambar styraciflua and Platanus occidentalis (Schultz, 1983) and Tecomella undulata (Jindal et al., 1992).

Table 2. Plant height, collar diameter, crown diameter and biomass of 30 accessions of P.alba over 3 years.

Accession number

Plant height (cm)

Collar diameter (cm)

Crown diam.(cm)

Biomass (kg)

1 yr

2 yr

3 yr

1 yr

2 yr

3 yr

28

EC 308109

42

104

215

0.95

2.11

3.94

358

5.76

57

EC 308112

43

88

186

0.88

2.02

3.80

331

5.59

65

EC 308119

60

102

225

1.06

1.76

4.19

383

7.05

66

EC 308120

52

98

192

1.06

1.81

2.33

254

4.21

67

EC 308121

47

87

259

0.79

1.31

3.78

348

2.39

68

EC 308122

56

78

169

0.88

1.41

3.32

299

4.62

70

EC 308123

49

93

185

1.01

1.90

2.90

316

4.04

71

EC 308124

59

92

181

0.95

1.78

2.87

347

5.23

72

EC 308125

50

98

173

0.90

2.48

3.41

311

6.75

73

EC 308126

43

88

249

0.63

1.39

3.76

340

3.80

74

EC 308127

49

72

126

1.13

1.90

1.99

260

1.84

75

EC 308128

61

112

186

0.92

1.57

2.97

308

2.67

78

EC 308129

36

100

224

0.97

2.31

4.36

390

4.59

120

EC 308130

44

103

261

0.93

1.81

3.92

324

4.15

122

EC 308132

54

88

167

0.95

1.66

2.31

254

2.69

126

EC 308133

58

123

231

0.94

2.11

3.48

329

6.04

128

EC 308135

53

96

184

0.82

1.78

2.95

311

5.09

135

EC 308141

50

91

168

0.87

1.39

2.91

324

2.91

144

EC 308142

42

82

198

0.98

2.00

2.73

330

3.80

145

EC 308143

44

82

179

0.97

1.86

3.12

303

4.80

146

EC 308144

40

100

154

0.81

2.22

2.76

305

7.84

147

EC 308145

43

104

220

1.09

2.24

4.07

365

5.81

148

EC 308146

39

67

141

0.79

1.19

2.52

256

3.43

149

EC 308147

41

68

151

0.89

1.54

2.38

289

2.38

150

EC 308148

46

76

202

0.94

1.48

3.46

379

4.71

151

EC 308149

42

104

208

1.01

2.15

3.48

379

6.30

152

EC 308150

38

67

160

0.87

1.42

2.78

277

2.21

153

EC 308151

46

74

153

1.14

1.78

2.58

291

2.82

230

EC 308154

42

84

179

0.84

1.69

2.84

353

4.35

233

EC 308156

40

73

133

0.66

1.26

2.12

284

2.26


Mean


47

90

189

0.92

1.78

3.14

320

4.34

± SE


5.51

12.6

39.16

0.15

0.39

0.84

49.25

1.59

Range


36-

67-

126-

0.63-

1.19-

1.99-

254-

1.84-



61

123

261

1.14

2.48

4.36

390

7.84

CV %


16.62

19.89

29.37

23.23

31.18

37.74

21.77

52.00

CD 5%


10.96

25.11

77.93

-

-

-

-

3.16

CD 1%


14.49

33.19

-

-

-

-

-

4.18

Table 3. Analysis of variance and genetic parameters, calculated as mean squares, for plant height (Ht.), collar diameter (SBD), crown diameter (Crown) and biomass of P. alba over 3 years (* p<0.05; ** p<0.01).

Source of variation

d.f Ht.

1 year old

2 year old

3 year old

3 year

3 year

SBD

Ht.

SBD

Ht.

SBD

Crown

Biomass

Replications

3

198.77

0.079

980.10

0.12

6588.67

4.21

7898.33

6.98

Accessions

29

198.27**

0.057

801.81**

0.45

4984.76*

1.68

6244.86

10.20**

Error

87

60.61

0.046

318.31

0.31

3066.83

1.40

4850.39

5.04

GCV


12.52

5.68

12.26

10.79

11.61

8.42

5.84

26.07

PCV


20.81

23.91

23.37

33.00

31.59

38.67

22.54

58.16

Heritability (%)


36.20

5.60

27.50

10.70

13.50

4.70

6.70

20.10

Genetic advance (GA)


7.27

0.03

11.88

0.13

16.59

0.12

9.96

1.04

GA as % of mean

15.52

3.26

13.25

7.30

8.80

3.82

3.11

23.96

Significant positive correlation coefficients between plant height and collar diameter across all growing periods indicated that selection practised for one trait will be automatically meaningful for a second trait and vice versa (Table 4). The associations were more pronounced with increasing age at all the three levels (genotypic, phenotypic and environmental). The magnitude of correlations at all three levels were similar after 30 months. Environmental correlations include the effects of soil heterogeneity and cultural irregularities, such factors causing harmonic changes in tree behaviour and may be easily interpreted in terms of physiological adjustments (Tewari et al., 1994).

The application of non-hierarchical Euclidean cluster analysis using plant height and collar diameter resulted in the formation of four clusters across all growing periods. The clustering pattern of different accessions changed with time (Table 5). Acc. no. 126 performed the best and remained in cluster IV throughout. The performance of acc. nos. 28 and 147 were relatively poorer after 6 months and so were positioned in cluster III, but they attained good growth in subsequent years and moved to cluster IV. Acc. nos. 65, 67, 73, 78 and 120 did not perform well in the first two growing periods, but by 30 months the had grown appreciably and as such they also moved to cluster IV. The degree of distance was found to be maximum between clusters I and IV across all the three growing periods (Table 6). However, the peak (3.48) observed after 30 months may perhaps be due to high variable values. For intra-cluster distances no particular trend was evident.

Table 4. Correlation coefficients between plant height and collar diameter of P. alba in 3 different years (*p<0.05; **p<0.01).


Genotypic

Phenotypic

Environmental

1991

0.037

0.372*

0.338

1992

0.478

0.658**

0.716

1993

0.876

0.821**

0.827

Table 5. Clustering pattern of 30 accessions of P. alba over 3 growing periods using non-hierarchical Euclidean cluster analysis.

Year no.

Cluster accs.

No. of accs. in cluster

Accessions

Cluster mean (cm)

Ht.

SBD

1991 I 8 57,73,146,148,149,152,230,233 40,62 0.80

II

5

67,68,72,128,135

51.15

0.85

III

11

28,70,74,78,120,144,145,147,150,151,153

57.29

0.98

1992

I

9

67,68,73,13,178,149,150,152,233

77.08

1.38

II

7

65,66,70,71,75,120,128

99.21

1.77

III

7

57,74,122,144,145,153,230

81.32

1.85

IV

7

28,72,78,126,146,147,151

104.71

2.23

1993

I

7

74,122,146,148,149,153,233

146.50

2.38

II

10

66,70,71,75,128,13,144,145,152,230

181.02

2.84

III

5

57,68,72,150,151

187.65

3.49

IV

8

28,65,67,73,78,120,126,147

235.28

3.94

Conclusions

The material used in the present investigation showed a wide range of variability and differential growth patterns, therefore early performance may not always mean similar performance levels in subsequent years and vice versa. The selection of accessions showing relatively better and consistent performance throughout the trial (e.g. acc. nos. 28, 65, 78, 120, 147 and 151) may be beneficial in terms of productivity in future plantations programmes. Similar findings have also been reported with P. cineraria (Kackar, 1988) and Tecomella undulata (Jindal et al., 1992), the two most prominent native species of the Indian arid tract.

Table 6. Average distance of cluster members from cluster centroids (diagonal) and distances between cluster centroids of four clusters having 30 accessions of P. alba in 4 different years.

Year

Cluster

I

II

III

IV

1991

I

0.83




II

1.57

0.54



III

1.85

1.68

0.79


IV

2.83

1.37

1.94

0.69

1992

I

0.70




II

1.96

0.54



III

1.42

1.28

0.56


IV

3.20

1.41

2.01

0.67

1993

I

0.53




II

1.21

0.42



III

2.08

1.03

0.50


IV

3.48

2.29

1.51

0.63

Acknowledgements

Funding support from the Indo-US, PL-480 project, grant no. FG-IN-749 is gratefully acknowledged. The authors also wish to thank Dr. A.S. Faroda, director of CAZRI, for providing all the necessary facilities as and when required.

References

Anonymous, 1987. Rajasthan Forest at a Glance. State Forest Department, Jaipur, India. 23p.

Champion, H.G. and S.K. Seth, 1968. A Revised Survey of Forest Types of India. Government of India Publication Branch, New Delhi, India. 404p.

Dhir, R.P., 1984. Soils of arid and semi-arid regions: their characteristics and properties. In: Shankarnarayana, K.A. (ed.) Agroforestry in Arid and Semi-Arid Zones. Central Arid Zone Research Institute, Jodhpur, India. pp20-29.

Doshi, S.P. and K.C. Gupta, 1991. SPAR 1: A statistical package for agricultural research data analysis. IASRI, New Delhi.

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Mann, H.S. and S.K. Saxena, 1982. Improvement of energy resources in Indian arid zone. In: P.K. Khosla (ed.) Improvement of Forest Biomass. Indian Society of Tree Scientists, Solan, India. pp283-292.

Mann, H.S. and K.D. Muthana, 1984. Arid zone forestry. CAZRI Monograph No. 23. Central Arid Zone Research Institute, Jodhpur, India. 48p.

Schultz, E. B., 1983. Genetic parameters and expected gains from open pollinated progeny test of sweet gum (Liquidambar styraciflua) and sycamore (Platanus occidentalis). Ph.D. Thesis, North Carolina State University. Forestry Abstracts 46: 657-658.

Sharma, N.K., L.N. Harsh, J.C. Tewari and M.D. Bohra, 1993. Variability and changes in genetic parameters for plant height in Prosopis pallida. Annals of the Arid Zone 32: 273-275.

Tewari, J.C., L.N. Harsh and J. Venkateswarlu, 1993. Some aspects of plantation forestry research in western Rajasthan. In: Dwivedi, A.P and Gupta, G.N. (eds.), Afforestation of Arid Lands. Scientific Publishers, Jodhpur, India.

Tewari, S.K., D. Pandey, V. Pande and S. Tripathi, 1994. Inter character correlation in Populus deltoides Bart. Indian Journal of Forestry 17: 61-63.


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