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UNIVERSITI PUTRA MALAYSIA EFFECTS OF LOGGING ON STREAKWATER QUALITY AND SOLUTE INPUT-OUTPUT BUDGETS IN SMALL WATERSHEDS IN PENINSULAR MALAYSIA ZULKIFLI YUSOP FSAS 1990 5

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Page 1: UNIVERSITI PUTRA MALAYSIA EFFECTS OF LOGGING ON ... · effects of logging on streakwater quality and solute input-output budgets in small watersheds in peninsular malaysia by zulkifli

 

UNIVERSITI PUTRA MALAYSIA

EFFECTS OF LOGGING ON STREAKWATER QUALITY AND SOLUTE INPUT-OUTPUT BUDGETS IN SMALL WATERSHEDS

IN PENINSULAR MALAYSIA

ZULKIFLI YUSOP

FSAS 1990 5

Page 2: UNIVERSITI PUTRA MALAYSIA EFFECTS OF LOGGING ON ... · effects of logging on streakwater quality and solute input-output budgets in small watersheds in peninsular malaysia by zulkifli

EFFECTS OF LOGGING ON STREAKWATER QUALITY AND SOLUTE INPUT-OUTPUT BUDGETS IN SMALL WATERSHEDS

IN PENINSULAR MALAYSIA

By

ZULKIFLI YUSOP

Thesis Submitted in Fulfilment of the Requirements for the Degree of Master of Science

in the Faculty of Science and Environmental Studies Universiti Pertanian Malaysia

December 19 90

Page 3: UNIVERSITI PUTRA MALAYSIA EFFECTS OF LOGGING ON ... · effects of logging on streakwater quality and solute input-output budgets in small watersheds in peninsular malaysia by zulkifli

ACKNOWLEDGMENTS

It gives me much pleasure to acknowledge and thank many

individu a l s and i nst itut ions for the ir s ig n i f i c ant

contributions during the entire course of this study .

1 wou ld l ike to express my s incerest thanks t o my

8upervisor , Dr Anhar Suki, for his original ideas , helpful

advice , guidance and stimulating diacussions . I am particularly

happy with and appreciate his approachable manner which made

this exercise a pleasant one . Similar appreciation is extended

to my co-supervisor , Hohd Fauzi Zakaria, for his constructive

comments on water chemistry.

Thanks are due to the Forest Research Institute Malaysia

( FRIM )

course

for giving me the opportunity to undertake

on a part-time baEli.s . The continuous interest

this

and

concern of the Director General of FRIM, Dato ' Dr Salleh Mohd

Nor , ia highly appreciated . Utmost thanks are extended to Dr

Abdul Rahim Hj Nik, my project leader at FRIM, for his

dedication and unstinting help; also for providing runoff and

rainfall data, without which my analyses of solute losses and

solute input-output budgets would not have been possible. I am

indebted to my colleagues, Baharuddin and Zainuddin for their

cooperation . The three-dimensional view and topographic map of

the study area were skillfully prepared by Saifuddin who

deserves my cordial thanks . My heartfelt acknowledgment

ia conveyed to Azman Haasan, a former assistant hydrologist ,

ii

Page 4: UNIVERSITI PUTRA MALAYSIA EFFECTS OF LOGGING ON ... · effects of logging on streakwater quality and solute input-output budgets in small watersheds in peninsular malaysia by zulkifli

for checking the English in a signif icant portion of the draft

manuscript . My s incerest thank goes to Dr Zelina Zaiton Ibrahim

for proof reading the whole manuscript .

Field and laboratory work were a.sisted by the re.earch

staff and foresters of the Hydrology Section , FRIM . They are

Mohd Sahat , Raj endran, Hashim, Ahmad Sahar, Alisbana , Renj er

Mohd Nor , Ibrahim, Yusaini, Nazri and Asna. Their earnestness

and hardwork were the decisive factors in making this study a

reality .

Many thanks are extended to the Chemistry Department ,

Petal ing Jaya , for the chemical analyses ; the Government of

New Z e a l and , for prov id ing f i nanc i a l a id in the initial

setting-up of the experimental catchment ; and the Forestry

Department for giving support and cooperation . I am also

grateful to lecturers and colleagues at Universiti Pertanian

Malaysia, Dr Na8iman, Dr Mohd Awang , Dr I8mail Yaziz , Dr

Ramdzani , En Mohd Kamil and Azman for their concern and for

sharing nice jokes .

Last but not least , heartfelt appreciation is due to my

dear w i f e , Fadhi l a h , tor her under standing , constant

encouragement and sacrifices ; and to my children, Zulfadli and

Zhafri for being an everlasting source of in.pirat ion . To my

parents , brothers and sisters , I wish them every success in

this world and hereafter under the guidance and in the path of

Allah s .w . t . Wassalam .

iii

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TABLB OF CO�S

Page

ACKNOWLEDGMENTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ii

LIST OF TABLES · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ix

LIST OF FIGURES · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xiv

LIST or PLATES · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xx

LIST OF ABBREVIATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xxi

ABSTRACT · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xxii

ABSTRAK · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xxiv

CHAPTER

I INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1

Background · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1

Obj ectives · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4

I I REVIEW OF LITERATURE 5

The Catchment aa a Planning Unit 5

History of Catchment Study in Malaysia 6

Impact of Man ' s Activities in Forested Catchments . 8

Sediment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8

Sediment Concentration . . . . . . . . . . . . . . . . . . . . 9

Sediment Yield . . . . . . . . . . . . . . . . . . . . . . . . . . 13

Sediment/Pol lutant Sources and Mechanisms of Transport . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 15

Physical Streamwater Quality 19

Chemical Quality and Hydrologic Nutrient Losses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 4

iv

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I I I

Page

Non-Hydrologic Nutrient Losses 33

Summary · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 35

Intra8Y8tem Proce8ses Affecting Water Chemistry and Nutrient Transfer . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 6

Hydrological Cycle . . . . . . . . . . . . . . . . . . . . . . . . 38

Litterfall • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 42

S UInlDary • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 44

Rainfall Chemistry . . . . . . . . . . . . . . . . . . . . . . . . . . . . 44

Rainfall Acidity . . . . . . . . . . . . . . . . . . . . . . . . . . . . 45

Sources of Rainfall Constituents 46

Maj or Ions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . � 47

Sulphate 48

Nitrogen 49

Phosphorous 50

Summary 5 1

Water Resource Management 5 1

Inst itutions 5 1

Legislation 53

Logging Guidelines 5 5

Summary 58

SITE DESCRIPTION 59

Location . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 59

Geology and Soil 64

Vegetation · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . 66

Climate · . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6 6

v

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IV

V

METHODOLOGY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Field Instrumentation . . . . . . . . . . . . . . . . . . . . . . . . .

Samplings . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Laboratory Analyses . . . . . . . . . . . . . . . . . . . . . . . . . .

Treatment of the catchments

Source and Treatment of Data

Statistical Approaches . . . . . . . . . . . . . . . . . . . . . . . . .

Two Sample Test

Regression on Dummy Variable

EFFECTS ON STREAMWATER QUALITY MATERIAL EXPORTS

AND

Temporal Variations . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

pH . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Specific Electrical Conductivity

Colour

Turbidity

Suspended Solids

Dissolved Solids

Alkalinity

Hardness . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Calcium and Magnesium

Iron . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Potassium

Sodium . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Ammoniacal-N and Nitrate-N

vi

Page

69

69

7 1

' 7 2

7 4

79

79

79

80

85

94

94

102

105

109

115

12 1

123

125

127

129

133

137

138

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VI

Page

sulphate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 141

Phosphate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 144

Silicate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 145

Chloride and Fluoride . . . . . . . . . . . . . . . . . . . . . 147

Comparison with Water Quality Criteria and Standards • • • • • • • • • • • • • • • • • • • • • . • • . • 149

Regression Analysis for Detecting Changes in water Quality . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 152

Variation with Discharge 163

Correlation between Parameters 170

Specific Electrical Conductivity . . . . . . . . . . . . . 170

S . E . C . and Major Ions 170

S . E . C . and Dissolved Solids 177

Total Hardness 178

Su spended Solids and Turbidity 181

Material Exports 183

Suspended Solids 183

Solutes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 190

Prediction of Solute Losses on Monthly Runoffs . . 208

Ionic Balances . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 14

RAINFALL CHEMISTRY 2 17

pH . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 17

Major Ions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 2 1

Nitrogen and Phosphorus 2 2 6

Relationships between Solute Concentrations and Rainfall . . . . . . . . . . . . . . . . • . . . . . . . . . . . . . . . 227

Relationships between Solute Loads and Rainfal l . . 228

vii

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VII

VIn

SOLUTB BUDGBTS ANALYSES . . . . . . . . . . . . . . . . . . . . . . .

Basic Cations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Nitrogen . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Sulphate and Phosphate . . . . . . . . . . . . . . . . . . . . . . .

Chloride . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

SUMMARY AND CONCLUSIONS

SWM\ary

Conclusions

. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Future Research Considerations

BIBLIOGRAPHY

VITA . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

viii

Page

233

233

235

243

244

245

245

252

253

255

306

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Table

1

2

3

LIS!r OF !rABLES

Mean of Stream Sediment Concentrations in Und isturbed and Part i a l ly D i sturbed Catchments in Peninsular Malaysia • • • • • • . . . .

Sediment Yields from Forested and Disturbed Catchments in Peninsular Malaysia • . • • • . .

Erosion Rates and Skid-Trails in Indonesia

Runoffs on

4 Effects of Control Timber Harvesting on Stream Turbidities at Fernow Experimental

5

6

7

8

9

Forest . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Rat es o f N03- Lo s s e s Re su lt ing from

Clearcutting and other Destruct ive D iaturbance. . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Effects of Forest Conversion on Streamwater Qual ity at the Sungai Tekam Experimental Basin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Annual Chemical Influxes ( kg/ha ) via Rainf a l l , Through f a l l and Stemf low in Tropical Rainforest Sites

Total Litterfall and Nutrient Returns in Tropical Forest Sites • • • • • • • • • • • • • • • • • • • .

Water Resources-Related Enactments in Malaysia

Legislations and

10 Phys i ca l Characte r i st ics of the Three Catchments at the Berembun Experimental Watershed . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

11 Chemical contents at A-Horizon of Soil at the Berembun Experimental Watershed

12 Methods and Equipment Used for Laboratory

Page

11

14

17

22

30

32

41

43

S4

64

6S

Analyssa • • • • . . • • • . • • • • • • • . . • • • • • • . • • • • . • . . . . 73

13

14

Logging Prescriptions in the Supervised and Unsupervised Catchments at the BEW • • • • • • • • •

The Overall Mean Monthly Streamwater Quality during Calibration , Transition and Recovery Periods . . . . . . . . . . . . . . . . . . . . . . . .

ix

78

86

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Table

15

16

17

18

The Baseflow Mean Monthly Streamwater Qual ity during Calibration , Transition and Recovery Periods • . • . . . . . . . • . • . . . • . . . . . . . .

The Stormflow Mean Monthly Streamwater Quality during Cal ibrat ion , Transition and Recovery Periods . • • . . . . . • . • . • • • • • • • . . . . . .

Summary of the Two Sampl e Test for Detecting Changes in the Monthly Means of Streamwater Quality Parameters • • • • • • • • • • • . •

Two Sample Test for Detecting Differences between the Ba.ef low Month l y Means and Stormtlow Monthly Means • • • • • • • • • • • • • • • • • • • . •

19 Regression Analysis on Dummy Variables for Testing Logging Effects on Streamwater

Page

88

90

92

99

Quality . • . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 6 1

2 0 Regression Analysis o f Streamwater Concentrations/Values against Instantaneous

2 1

Discharge ( l/s ) • • • • • • • • • • • • • • • • • • • • • . • • • • • . • 165

Corre lat ion P arameters Calibration

Analys i s for in Cat c hment

Streamwater One du ring

Period . . . . . . . . . . . . . . . . . . . . . . . . . 173

22 Correlation Analys i s for Streamwater

2 3

24

2 5

2 6

2 7

Parameters in Catchment Two during Calibration Period • • • • • • • • • • • • • • • • • • • • • • • . • • 174

Corre lation Analys i s for Streamwater Parameters in Catchment Three during Calibration Period • • • • • • • • • • • • • • • • • • • • • • • . .

Correlation between Suspended Solids (mgtl ) and Turbidity ( NTU) for Prelogging and Post logging Periods • • • • • • • • • • • • • • • • • . •

Annual Exports of Solutes ( kg/ha ) from the Three Catchments • • • • • • • • • • • • • • • • • • • • • .

Regression Analysis Using Dummy Variable for Detecting the Effects of Logging on Monthly Solute Loads • • • • • • • • • • • • • • • • • • • • . .

Summaries of Regression Analysis between Solute Loads ( kg/ha/mth ) and Runoffs (mm) during Pre logging and Post logging Periods

x

175

182

202

203

2 10

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Table

2 8

29

30

3 1

32

33

34

35

3 6

37

38

39

40

41

42

Ionic Composition of the Streamwater ( maq/ l ) during Calibration , Tran.ition and Recovery Periods • • • • • • • • • • • • • • • • • . •

Rainfal l Chemi stry at t he Berembun Experimental Watershed • • • • • • • • • • • • • • • • • • • • . •

Corre l at ion Analys i s for Ra in f a l l Component s a t t he Berembun Experiment al Water.hed . . . . . . . . . . . . . . . . . . . . . . . . • . . . . . . .

I on i c Compos i t ion of Ra i n f a l l at the Berambun Bxperimental Watershed • • • • • • • • • • •

Regression Analysis of Evently Solute Loads ( kg/ha ) on Rainfall Depths (mm) . . . . . .

Regression Analysis of Monthly Solute Loads ( kg/ha/mth ) against Rainfall Depths ( mm )

Annual Atmospheric Some Tropical Areas

Nutrient ( kg/ha )

Loadings of

Solute Input-Output Budgets ( kg/ha/yr ) at the Berembun Experimental Watershed • • • • • • .

Solutes I nput-Output Budget s for Some Tropical and Temperate Catchments • • • • • . • • . •

An Example of Data Arrangement for Performing Regression on Dummy Variables

Criteria and Standards for Drinking Water

Regression on Dummy Variables for Detecting Changes in N03-N Concentrations ( mg/ l ) in Cl . . • . . . • . • . . • . . . . . . . . . . . . . . • . . . . . . . . .

Regres.ion on Dummy Variables tor Detecting Change. in ( Log ot) Pe Concentrations (mg/ l ) in Cl . • . • • . . . • . . . . . . . . . . . . . . • . . . . . . .

Regression on Dummy Variables for Detecting Changes in Potassium Concentrations ( mg/ l ) in Cl . . • • • • . . • • • . . . . . . . . . • • . . . . . • • . . . . . . .

Regression on Dummy Variables for Detecting Changes in Potassium Concentrations (mg/ l ) i n C3 • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • •

xi

Page

2 1 5

2 1 8

222

223

230

231

232

236

237

283

284

285

286

287

288

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Table

43

44

45

46

47

48

49

50

51

52

53

54

55

Regress ion Fitting Results for Log ( S . E . C . ) against Ions in Cl . . . . . . . • . . . . . . . . . . . . . .

Regress ion Fitting Results for Log ( S . E . C . ) against Ions in C2 • . • • • • • • • • • • • • • • • • . • . .

Regression Fitting Results for Log ( S . E . C . ) against Iona in C3 • . . . • . . • • • • • . . . . . . . . . •

Model Fitting Results of S . S . Losses ( SL ) against Hydro logical Var i ab l e s for Cl during Calibrat ion Period • • • • . • • . • • • • • .

Kodel Fitting Results of S . S . Losses ( SLI against Hydro logical Var iab l e s for Cl during Transition Period • • • • • • • • • • • • • . . •

Model Fitting Results of S . S . Losses ( SL ) against Hydro logical Vari ab l e s for C l during Recovery Period • • • • • • • • • • . • • • • • •

Kodel Fitting Results of S . S . Losses ( SL ) against Hydro logical Variabl e s for C2 during Calibration Period • • • • • • • • • • • • . . •

Model Fitting Results of S . S . Losses ( SL) against Hydro logical Variab l e s for C2 during Transition Period • • • • • • • • • • • • • • • •

Model Fitting Results of S . S . Losses ( SL ) against Hydro logica l Variab l e s for C2 during Recovery Period • • • • • • • • • • • • • • • •

Kodel Fitting Results of S . S . Losses ( SL ) aga inst Hydro log ical Var iab l e s for C3 during Cal ibration Period . • • . • • • • • • • . • • . •

Kodel Fitting Results of s . s . Losses ( SL) against Hydro logical Var i ab le s for C3 during Transition Period • • • • • • . • • . . . •

Kodel Fitting Results of S . S . Losses ( SL ) again st Hydro logical Var iab l e s for C3 during Recovery Period . • • • • • • • • • • • • . • • .

Regres sion on Dummy Variables for Detecting Changes in N03-N Loads from Cl • • • • • • • • • . •

xii

Page

289

289

290

291

291

292

292

293

293

294

294

295

296

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Table

56

57

58

Chow Test for Detecting D i f ferences in Regre.sion Lines for Pre logging and Postlogging Periods ; Monthly Potassium Losses vs . Monthly Runoffs in C2 • • . • . • • . . • .

Chow Test Regression P08tlogging Losses vs .

for Detecting D i f ferences in Lines for Pre logging and

Periods ; Monthly Potassium Monthly Runoffs in C3 • • • • • . • • • .

Conversion Factors from Molar Miliequilibrium ( meq/ l ) units

( mg/ l ) to

xiii

Page

297

299

30 1

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Figure

1

2

3

4

5

6

7

8

9

10

11

12

13

14

LIST OF FIGURES

An Ecosystem Model Showing Nutrient Flux and Biogeochemical Processes • • • • • • • • . • • •

Locat ion o f t he Study S it e and its Surrounding Landuse Patterns • • • • • • • • • • • • • • . •

Layout o f Watershed

the Berembu n Experiment al . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Three-Dimensional View of the Berembun Experimental Watershed • • • • • • • • • • • • • • • • • . . • •

Topographic Map of Experimental Watershed

the Berembun

Monthly Rainfall Pattern at the Berembun Experimental Watershed, July 1980 to June 1988 . . . . • . • • • • • • . . . . . . . . . . . . . • • . . . . . . . . .

Overall Monthly Means Variation of pH in Cl , C2 and C3 . • . . . . . . . • . . . . . . . . . • . . . . . . . .

Relationships between the Monthly Overall Means of pH , Conductivity and Rainfall in C1 during Cal ibration Period • • • • • • • • • • • • • . •

Frequency D istr ibut ion Curve s for I nstant aneou s Va lues of pH in C1 , C2 and C3 • • . • • • • • • • . . • • • • . • • . • • . • • • . • . . . • .

Basef low Month ly Means Variat ion of Conductivity in C1, C2 and C3 • • • • • • . . • • • . .

Frequency D i str ibut ion Curve s for I nstant aneous Values of Conduct ivity in el, C2 and C3 . . . . . . . . . . . . . . . • . . . . . . . . . .

Overall Monthly Means Variation of Colour in C1 , C2 and C3 . . . . . . • . . • . . • . . . . . . . .

Frequency D i stribut ion Curves for Instantaneous Values of Colour in C1 I C2 and C3 • . . . • . . • . . . . . • . . . . . . . • . • . . • • . . . . . . . .

Overa l l Monthly Means Turbidity in C1 , C2 and C3

xiv

Var iation of . . . . . . . . . . . . . . . . .

Page

3 7

6 0

61

62

63

67

96

97

101

103

104

107

108

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Fiqure

1 5 Relationships between Monthly OVerall Mean o f Suspended Sol ids , Turb idity and Rainfall Depth in C1 during Calibration

Page

Period • • . . • • . . . . • . • . . . . . . . . . • . . • . . • . . . . • . . . . 112

16 Frequency D istribut ion Curve s for Instantaneous Values of Turbidity in C1 , C2

17

18

19

20

2 1

2 2

2 3

and C3 • . • • • • • • . . • . • • . • • • . . . . • • • • . • . . . . . . . . . . 113

Basef low and Stormflow Mont hly Means Variation of Turbidity in C1 • • • • • • • • • • . • . •

Overa l l Mont hly Mean Concentrat ions o f Suspended Solids i n Cl , C2 and C 3 • • • • • • • • •

Frequency D istr ibut ion Curve s for Instantaneous Values of Suspended Solids Concentrations in C1 , C2 and C3 • • • • • • • •

Basef l ow and Stormf low Mont hly Mean Concentrations of Suspended Solids in C1

Overal l Monthly Mean Concentrat ions o f Dissolved Solids in C1 , C2 and C3 • • • • • • . •

Overal l Monthly Mean of Alkalinity Levels in Cl , C2 and C3 . . . . . . . . . . . . . . . . . . . . . . . . . . .

Overall Monthly Mean of Hardness Levels in Cl , C2 and C3 • . . . . . . . . . . . . . • • . • . . . • . . . . . . . . .

114

l l7

118

119

122

124

126

24 Relationships between the Overal l Monthly Mean Concentrations of Calcium, Magnesium and Hardnes s in C1 during Cal ibration

2 5

2 6

2 7

28

Period . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 128

Overall Monthly Mean Concentrations of Iron in Cl , C2 and C3 . . . . . . . . . . . . . . . . . . . . . .

Frequancy D istribut ion Curve s for Instantaneous Value of Iron Concentrations in Cl , C2 and C3 . . . . . . . . . . . . • . . . . . . . . . . . . . . .

B as a f low and Stormf low Mont hly Mean Concentrations of Iron in C1 • • • • • • • • • • • • . . .

Basef low Monthly Mean Concentrat ions o f Potassium i n Cl , C2 and C 3 • • • • . . • • . • . .

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130

131

132

135

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Figure

2 9

3 0

3 1

Frequency D i .tribut ion Curves f or I n.tant aneou. Value of Pot a s s i um Concentrations in Cl , C2 and C3 • • • • • • • •

Overa l l Month ly Mean Concent rat ions of Nitrate-N i n Cl , C2 and C3 • • • • • • • • • • • . • • . . •

Overa l l Monthly Mean Concent rat ions of Sulphate i n Cl , C2 and C3 • • • • • • • • • • • • • • • • •

3 2 Inverse Relationship between Sulphate and pH Mont hly Mean Va lues , and Re latively Constant in Iron Concentration to Explain t he Oxi dat ion o f Pyrite during Drought

Page

136

140

142

Period . . . . . . . . . • • . . . . . . . • . . • . . • . . . . . . . . . . . . . 143

3 3

3 4

3 5

36

37

38

39

40

41

Overa l l Monthly Mean Concent rat ions of Silicate i n Cl , C2 and C3 • • • • • • • • • • • • • • • •

OVerall Monthly Mean Chloride in Cl , C2 and

Concentrations of C3 • • • • • • • • • • • • • • •

Regression Lines of Overall Monthly Mean Concentrations of Nitrate-N ; Cl against C2 • . .

Regression Lines of Overall Monthly Mean Concentrations of Nitrate-N ; C3 against C2 . . .

Regression Lines of Overall Monthly Mean Concentrat ion of Potassium; Cl against C2 . . •

Regress ion Lines of Overall Monthly Mean Concentration of Potassium; C3 against C2 . • .

Regression Lines of Overal l Monthly Mean Concentration of Sil icate ; Cl against C2 • . .

Regression Lines of Overal l Monthly Mean Concentration of Ironl Cl against C2 • . •

Relat ionships between pH , Conductivity and Turbidity Valu •• ) against Di.charge

A l ka l init y , ( Instantaneous . . . . . . . . . . . . . . . .

42 Relationships between Sodium, Calcium, Iron and Chloride ( Instantaneous Values) against

146

148

153

153

155

155

156

156

167

Di8charg8 • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 168

43 Correlation between Hardness and Sum of Calcium and Magnes ium . . . . . . . . . . . . . . . . . . . . . . 180

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Figure

44

45

D i f ference. in Mont hly Suspended So l ids Export. between C1 and C2 • • • • • • • • • • •

D i f ference. in Mont hly Suspended So l id . Export. between C3 and C2 • • • • • • • • • • .

46 Differences in Monthly Potassium Exports

Page

186

186

between C1 and C2 • . • • • • • . • • • • • • • • • • . • • . • • . . • 191

41 D ifferencea in Monthly Potassium Exports between C3 and C2 • • • • • • • • • • • • • • • • • • • • • . • • . . • 191

48 D i f ferences in Mont h l y Calc ium Export s between C l and C2 • • • • • • • • • • • • • • • • • • • • • • • • • • . 192

49

50

51

52

53

54

55

56

51

58

59

D i f ferencea in Mont hly Cal c ium Export s between C3 and C2 • . . . . . . . . . . . . . . . . . . . . . . . .

D i f ference. in Mont hly Sod ium Export s between Cl and C2 • • • • • • • • • • • • • • • • • . • • . . • . . . .

D i f ferences in Monthly Sod ium Exports between C3 and C2 • • • • • • • • • • • • • • • • • • • • • • . . • •

Differences in Monthly Magnesium Exports between Cl and C2 . . • . • . • . . . . • • . . • • . • • . . • . . .

Differences in Monthly Magnesium Exports between C3 and C2 • • • . . • • • • . • • • • • • . • • • . . • . . •

D i f ferences in Month l y S i l icat e Exports between Cl and C2 . . • • . . . • • . . . . . . • . • • . . . . . .

D i f ferences in Mont hly S i l ic ate Exports between C3 and C2 . . . • . . . . . . . . . • • • • . . . . . . . .

Differences in Monthly Iron Exports between Cl and C2 • . . . • • . • . . . • • • . • • • . • • . • • • . • • . . .

Differences in Monthly Iron Exports between C3 and C2 • • • • • • • • • • • • • • • • • • • • • • • • • • . . • • . • .

D i f ferencea in Mont h l y Chlor ide Expor t s between C 1 and C2 • • • • • • • • • • • • • • • • • • • • • • • . • •

D i f ferences in Mont h l y Chlor ide Export s between C3 and C2 • • • • • • • . • • • • • • • . • • • • • • • • .

xvii

192

193

193

194

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Figure

60

6 1

62

63

64

65

66

67

68

69

70

71

72

73

74

75

Differences in Monthly Nitrate-N Exports between Cl and C2 . . . . . . . . . . . . • • . • . . . . • • . . . .

Differences in Monthly Nitrate-N Exports between C3 and C2 • • • • • • • • • • • • • • • • • • • . • • • • . •

Dif ferences in Monthly Ammoniacal-N Exports between C1 and C2 • • • • • • • . • • • • • • • • • • • . • • • . . .

Dif ferences in Monthly Ammoniacal-N Exports between C3 and C2 . • • • • • • • . • • • • . • . • • . . • . • • . .

Dif ferences in Monthly Phosphate Exports between Cl and C2 . • • • . . • • . . • • • • • • • • • • . . • • . .

Dif ferences in Monthly Phosphate Exports between C3 and C2 . . . . . . . . . • • . • • • . . • • • . . • . . .

Regression Lines of Monthly Nitrate-N Exports ; C1 against C2 . . . . . . . . . . . . . . . . . . . . .

Regression Lines of Monthly Nitrate-N Exports ; C3 against C2 · . . . . . . . . . . . . . . . . . . .

Regr ••• ion Lin •• of Monthly Potaaaium Export. ; C1 against C2 · . . . . . . . . . . . . . . . . . . .

Regression Lin •• of Monthly Potassium Exports ; C3 against C2 · . . . . . . . . . . . . . . . . . . .

Regre s s ion Lines o f Month l y Pot as s ium Exports against Monthly Runoffs in C2 for Prelogging and Post logging Periods • • • • • • . •

Regre s s ion L i ne s of Mont h ly Pot a s s ium Exports against Monthly Runoffs in C3 for Pre logging and Post logging Periods • • • • • • • •

Monthly Mean Concentrations of Sulphate, Calcium and Magnesium in Rainwater • • • • • • • •

Monthly Me an Concentrations o f Sod ium , Chloride and Potassium in Rainwater • • • • • • . •

Monthly Mean Concentrations of Ammoniacal­N, Nitrate-N and Total-N in Rainwater • • • • •

Monthly Mean Concentrat ions of Phosphate in Rainwater . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

xviii

Page

198

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200

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204

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205

2 13

2 13

2 19

2 19

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220

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Figure

7 6

77

Normal Probability Plot of ( Log of ) S . E . C . Residuals . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

Residual Plot of ( Log of ) S . E . C . on the Predicted ValuBs • . . • • . . • . . . . . . . . • • . . . . .

xix

Page

303

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Plate

1

LIST OF PLATES

Page

V-Notch We ir and Steven-F Water Level Recorder for Measuring Streamflow Volume • • . • 70

2 Cross-drain Instal led at 450 - 600 along L099 inq Road • • • • • • • • • • • • • • • • • • • • • • • • • • • • 7 5

3 Hollow Log Installed in Stream to Minimise

4

5

6

Damage • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 76

Extraction of Log Using Crawler Tractor on Skid-trail . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

A Winch Lorry or "San Tai Wong" Used to Carry Logs to a Log-yard • • . • • • • • • • • • • • • • • •

Typical Regeneration of Pioneer Species on Skid-trai l , One and a Half Years after L099 ing . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

xx

77

77

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LIST or ABBREVIATIONS

pH in pH unit.

S . E . C . - spec i f ic e lectrical condu c t ivity ; u S / cm (micro-Siemen per centimeter at 2 SoC )

Turb . Turbidity; N . T . U . ( nephelometric turbidity units )

Colour - True colour, Hazen

S . S . Suspended solids , mg/ l

D . S . Dissolved solids , mg/ l

Alka . Total alkalinity ; mg/ l as caco3

Hard. Total hardness ; mg/ l as Caco3

ca2+ Calcium; mg/ l

Mg2+ Magnesium; mg/ l

Fe Iron; mg/ l

K+ Potassium; mg/ l

NH3-N Ammoniacal-nitrogen ; mg/ l

N03-N Nitrate-nitrogen; mg/ l

S042 - Sulphate ; mg/ l

po42- Phosphate; mg/ l

S i02 Silicate ; mg/ l

Cl- Chloride ; mg/l

F- Flouride ; mg/ l

m. a . s . l . meter above sea level

r Coefficient of correlation

r2 coefficient of determination

R2 Coef ficient of mu lt iple determination

R2adj Adj usted coefficient of mu ltiple determination

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S . D . Standard deviation

S . E . Standard error o f estimate

D . W . Durbin Watson statistic

N No of sample or correlation

SSR Sum of square due to regression

MSE Mean square error

Sg . Sungai , a Malay word meaning river

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Abetract of the theeie eubalitted to the Senate of Universiti Pertanian Malayeia in fulfilment of the requirements for the Degree of Kaeter of Science .

racultJ'

BmCTa or LOGGING ON STREAMWADR QUALIft AIID SOLUTB INPUT-OUTPUT BUDGETS

III IKALL WADllSBBDS III PBIIIHSUL&R MALAYSIA

by

IULJtIrLI YUSOP

July 1990

, Dr. Anhar Suki

, Science and Environmental Studies

The ef fecte of eelective logging on streamwater quality

and eo lute budget s were invest igated u s i ng t hree sma l l

catchmente : Cl , C2 and C3 . After a three-year cal ibration

per iod , C l and C3 were logged us ing " un supervi s ed " and

" supervised " logging methods respectively, whereas C2 was left

as control . Several control measures were imposed in the

supervieed C3 but none in the uneupervised Cl .

During the cal ibration period the levels for most of the

streamwater qua l ity paramet ers measured were within t he

standards for potable water . The exceptions were colour,

turbidity and iron. Significant increases in pH , specific

e lectrical conductivity , hardne s s , su spended sol ids ,

alkalinity, turbidity, diBsolved solids, silicate , calcium,

iron, and eodium were recorded in the unsupervised Cl . The

levels for colour and nitrate were also elevated initially but

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recovered to background values within a year . In contrast , in

the supervised e3 , signif icant changes were detected only for

hardness , magnes ium and iron. The impact of logging was

enhanced during the wet months especially for suspended solids ,

turbidity and iron .

Export of suspended solids during the cal ibration period

ranged from 0 . 08 to 0 . 24 mt/ha/yr . These levels increased

twenty-fold for Cl and two- fold for C3 during the first year

after logging . The monthly losses of most solutes also

increased significantly for both Cl and C3 but the magnitude

of loss was much greater for the former . The losses of calcium ,

potassium and magnesium showed a tendency to increase over time

whereas the increases in nitrate losses were short-l ived .

Rainfall samples contained low levels of anthropogenic

pol lutants and were affected more by terrestrial sources . The

inputs of nutrients from rainfall constituted , on the average :

64\ , 5 5 \ , 40\ and 2 5 \ of the outputs of potassium, calcium ,

sodium and magnesium respectively. However , the inputs o f

calc ium and magnes ium were calculated based o n data of a

previous study conducted at a nearby site , Pasoh .

The results of the study show that proper control measures

substantially reduce the effects of logging on streamwater

quality and solutes losses . Further detail studies may provide

better indications on the effectiveness of specific control

measure .

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