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RESTORING RIPARIAN VEGETATION –
A PROMISING MEANS TO ENSURE CLEAN WATER
Kamal Melvani,
Neo Synthesis Research Centre, Sri Lanka,
email: neosynth@sltnet.lk
SURFACE WATER
Riparian zones
can be broadly
defined as the
land that
adjoins or
directly
influences a
body of water
(Price & Lovett 2002)

Paradeke Oya, Gampola
Structure and characteristics of riparian lands
Riparian ecosystems:
• Shade and lower stream temperatures
• Filter and sorb pollutants
• Provide areas for sediment deposition
• Promote microbial decomposition of organic
matter and nutrients
• Minimize stream bank erosion
• Provide habitat for biodiversity
• Open wildlife corridors
• Enhance infiltration replenishing groundwater
• Increase reservoir life (Chin 2012)
Major components of riparian vegetation that affect stream water chemistry

(Dosskey et al. 2010)
Soil Organic Matter is a
biomembrane that filters
pollutants,
reduces
sediment load in rivers,
degrades
contaminants,
and is a major sink for
atmospheric CO2 and CH4
(Lal, 2004)
Processes through which major components of vegetation
in riparian ecosystems affect stream water chemistry

(Dosskey et al. 2010)
• Deep rooted trees in biologically active zones
remove Nitrates in shallow ground water.
Hydraulic residence time critical (Melvani, 2011).
• Nitrate removal minimal when water moves to
regional groundwater and emerges as base
flow(Dosskey et al. 2010).
• For sediment borne P retention, fine sediment
control coupled with use of vegetation, can
increase P uptake into plant tissue (Dosskey et al. 2010)
• However, riparian forests have low net dissolved P
retention (Dosskey et al. 2010).
• Non nutrient chemicals absorbed from soil by plant
roots. Heavy metals (e.g., Cd, Cr, Hg, Ni, Pb),
metalloids (e.g., As, Se), and other elements (e.g.: B,
Cs, Sr) (Dosskey et al. 2010).

• Riparian buffers could reduce electrical
conductivity (Melvani, 2011).
Riparian zone destruction
Illicit felling, dumping ground for garbage and erosion

Lemastota Oya, Haputale
Restoration
•

Riparian forest buffer systems (RFBS)
reduce Non Point Source pollution after it leaves
source area but before it reaches the stream

•

important on 1st and 2nd order streams where
intense interaction between terrestrial and
aquatic ecosystems occurs

•

slope of the RFBS main factor limiting the
effectiveness of sediment removal

•

use of native vegetation a key factor (Lowrance & Vellidis 2004).
Vegetated riparian zones can
strongly influence the chemical
contents of adjacent
streams, particularly through the
removal of nutrients
in runoff from agricultural uplands
Maragala Oya, Maragalakanda, Moneragala

RESTORATION WITH COMMUNITY
Riparian forest buffers for gullies in forest
gardens on Maragalakanda, Moneragala

Arumugam’s forest garden
Arumugam’s gully restored

Before

After

Jane Nona’s garden
Podisingho’s garden with Spathyphyllum patini planted on stream bank
Maha Oya, sub catchment
in Great Valley, Deltota
Planting in year 1

RESTORATION WITH PRIVATE COMPANY
Contour
Restoration of the riparian zone of Lake Richmond through Landcare
CLEARING GULLY

PLANTED
GULLIES

PLANTING GULLY
Gully C - School

Gully D

Gully E

Around the
Lake

Total plants

Ankenda
Hana
Heen Aratta
Maha Aratta
Green Bamboo
Yellow Bamboo
Thel Keena
Cassia
Star apple
Pinna
Thebu
Tree fern
Erabadu
Mora
Kotadimbula
Forest species
Goraka
Wild Ginger
Rathu Kenda
Wild Impatiens
Beeriya
Wild Tobacco
Bukenda
Nika dawula
Sapu
Malaboda
Kududawla
Dawul Kurundu
Forest bamboo
Heen Bowitiya
Pavatta
Karanda
Nelu
Damba
Alubo
Heen Damba
Gadumba
Sawan Idala

Gully C

Aconychia pedunculata
Agave rigida var. sisalana
Alpinia calcarata
Alpinia zerumbet
Dendrocalamus giganteus
Bambusa vulgaris
Calophyllum tomentosum
Cassia spectabilis
Chryssophyllum cainito
Clerodendrum chinense
Costus specious
Cyathea sp.
Erythrina lithosperma
Euphoria longana
Ficus hispida
Forest species
Garcinia quaesita
Hedychium coronarium
Homolanthus populifolius
Impatiens sp.
Litsea ovalifolia
Lobelia nicotianifolia
Macaranga indica
Meliosma pinnata
Michelia champaca
Myristica dactyloides
Neolistea fuscata
Neolitsea cassia
Ochlandra stridula
Osbeckia lanata
Pavatta indica
Pongamia pinnata
Strobilanthes sp.
Syzygium assimile
Syzygium sp.
Syzygium umbrosum
Trema orientale
Wendlandia bicuspidata
Total Plants Established

Gully B - Lake
Down area

Common Name

Gully b - Upper
Lake area

Scientific Name

Gully a1
Upper Lake area

o Planting in micro watershed
4,724 trees and plants in 39+ native
and indigenous species were planted in
the micro watershed of Lake Richmond.

10
8
8

4

67

76

30

25

15

97

23
103

41
10

33
75
1

6
16

7
2
5

28
40

72
62

37

33

11

12

2

7

324
8
218
308
6
3
210
1
2
13
19
1
3
0
22
444
10
510
347
2
126
18
134
3
90
161
172
216
15
40
6
53
667
93
3
19
1
6
4274

1
13

2
1

1

12

1
20

84
1

2
2
2

4
1
3

34
1
84
44
12
1
2

7
87

85

1
1
30
10

6
29

21

15
3

9
83

1
2
3
5
2
1
1
1
1
6
3
89

14
13
5
15
10
4

13
40
61
4
1

1
59
21

90
3

1

3

1

1
365

581

1
290

31
4
67
13
2
11

8

20

38

1

42
16
60

15
27
25
30

4
13
8
17

4
26
7
12

4
4
8
27

44
63
78
53

3

29

60
4

26
51
33

1

6

2
430

1193

70

62
11

58
3
97
31

121
1
170
83

6

19

2
1
150
13
1
7
1
2
690

11
63
14
1

344

11
105
5
1

381
Ground Water
Bioremediation

Kalmunai
Kalpitiya
2003

Dense planting round
the well with deep
rooted, native trees
forming a ‘root mat ’
below the surface to
uptake
the
contaminants.
0
Feb ' 4
April '04
June '4
August '04
Sept '4
October' 04
Nov '4
December' 04
Jan' 5
February'5
March'5
April'5
May'5
June'5
July'5
August'5
Sept'5
Oct'5
Nove'5
Dec'5
Jan'6
Feb'6
March'6
April'6
May'6
June'6
July'6
Aug'6
Sept'6
Oct'6
Nov'6
Dec'6
Jan'7
Feb'7
March'7
April'7
May'7
June'7
July'7
Aug'7
Sept'7
Oct'7
Nov'7
Dece'7
Jan'8
Fed'8
March'8
April'8
May'8
June'8
July ' 8
August'8
Sept'8
Oct'8
Nov'8
Dece'8
Jan'9

Concentration of N-N03 in mg/l

Concentration of N-No3 over time

80

70

60

50
Lower Well

40

30

20
Upper Well

10

Concentration of Nitrate Nitrogen over time
Electrical Conductivity at 250C over time
References
Chin, DA 2012, Water-Quality Engineering in Natural Systems : Fate and Transport
Processes in the Water Environment, 2 edn, Wiley, New York.
Dosskey, MG, Vidon, P, Gurwick, NP, Allan, CJ, Duval, TP & Lowrance, R 2010, 'The Role
of Riparian Vegetation in Protecting and Improving Chemical Water Quality in
Streams1', JAWRA Journal of the American Water Resources Association, vol. 46, no. 2,
pp. 261-77.
Lal, R 2004, 'Soil Carbon Sequestration Impacts on Global Climate Change and Food
Security', Science, vol. 304 no. 5677 pp. 1623-7.
, R & Vellidis, G 2004, 'Riparian forest buffers: hype? Or the silver bullet for NPS
pollution control?', Resource: Engineering & Technology for a Sustainable World, vol.
11, no. 10, p. 7+.
Melvani, K 2011, 'Bioremediation of Nitrates in Ground Water', M.Sc. thesis,
University of Peradeniya
Price, P. and Lovett, S. 2002, ‘Managing riparian land’, Fact Sheet 1, Land & Water
Australia, Canberra
Thank you!

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Unit-V; Pricing (Pharma Marketing Management).pptx
 

Session 6.5 restoring riparian vegetation

  • 1. RESTORING RIPARIAN VEGETATION – A PROMISING MEANS TO ENSURE CLEAN WATER Kamal Melvani, Neo Synthesis Research Centre, Sri Lanka, email: neosynth@sltnet.lk
  • 3. Riparian zones can be broadly defined as the land that adjoins or directly influences a body of water (Price & Lovett 2002) Paradeke Oya, Gampola
  • 4. Structure and characteristics of riparian lands
  • 5. Riparian ecosystems: • Shade and lower stream temperatures • Filter and sorb pollutants • Provide areas for sediment deposition • Promote microbial decomposition of organic matter and nutrients • Minimize stream bank erosion • Provide habitat for biodiversity • Open wildlife corridors • Enhance infiltration replenishing groundwater • Increase reservoir life (Chin 2012)
  • 6. Major components of riparian vegetation that affect stream water chemistry (Dosskey et al. 2010)
  • 7. Soil Organic Matter is a biomembrane that filters pollutants, reduces sediment load in rivers, degrades contaminants, and is a major sink for atmospheric CO2 and CH4 (Lal, 2004)
  • 8. Processes through which major components of vegetation in riparian ecosystems affect stream water chemistry (Dosskey et al. 2010)
  • 9. • Deep rooted trees in biologically active zones remove Nitrates in shallow ground water. Hydraulic residence time critical (Melvani, 2011). • Nitrate removal minimal when water moves to regional groundwater and emerges as base flow(Dosskey et al. 2010). • For sediment borne P retention, fine sediment control coupled with use of vegetation, can increase P uptake into plant tissue (Dosskey et al. 2010)
  • 10. • However, riparian forests have low net dissolved P retention (Dosskey et al. 2010). • Non nutrient chemicals absorbed from soil by plant roots. Heavy metals (e.g., Cd, Cr, Hg, Ni, Pb), metalloids (e.g., As, Se), and other elements (e.g.: B, Cs, Sr) (Dosskey et al. 2010). • Riparian buffers could reduce electrical conductivity (Melvani, 2011).
  • 11. Riparian zone destruction Illicit felling, dumping ground for garbage and erosion Lemastota Oya, Haputale
  • 12. Restoration • Riparian forest buffer systems (RFBS) reduce Non Point Source pollution after it leaves source area but before it reaches the stream • important on 1st and 2nd order streams where intense interaction between terrestrial and aquatic ecosystems occurs • slope of the RFBS main factor limiting the effectiveness of sediment removal • use of native vegetation a key factor (Lowrance & Vellidis 2004).
  • 13. Vegetated riparian zones can strongly influence the chemical contents of adjacent streams, particularly through the removal of nutrients in runoff from agricultural uplands
  • 14. Maragala Oya, Maragalakanda, Moneragala RESTORATION WITH COMMUNITY
  • 15. Riparian forest buffers for gullies in forest gardens on Maragalakanda, Moneragala Arumugam’s forest garden
  • 17. Podisingho’s garden with Spathyphyllum patini planted on stream bank
  • 18. Maha Oya, sub catchment in Great Valley, Deltota
  • 19. Planting in year 1 RESTORATION WITH PRIVATE COMPANY
  • 21. Restoration of the riparian zone of Lake Richmond through Landcare
  • 23.
  • 24. Gully C - School Gully D Gully E Around the Lake Total plants Ankenda Hana Heen Aratta Maha Aratta Green Bamboo Yellow Bamboo Thel Keena Cassia Star apple Pinna Thebu Tree fern Erabadu Mora Kotadimbula Forest species Goraka Wild Ginger Rathu Kenda Wild Impatiens Beeriya Wild Tobacco Bukenda Nika dawula Sapu Malaboda Kududawla Dawul Kurundu Forest bamboo Heen Bowitiya Pavatta Karanda Nelu Damba Alubo Heen Damba Gadumba Sawan Idala Gully C Aconychia pedunculata Agave rigida var. sisalana Alpinia calcarata Alpinia zerumbet Dendrocalamus giganteus Bambusa vulgaris Calophyllum tomentosum Cassia spectabilis Chryssophyllum cainito Clerodendrum chinense Costus specious Cyathea sp. Erythrina lithosperma Euphoria longana Ficus hispida Forest species Garcinia quaesita Hedychium coronarium Homolanthus populifolius Impatiens sp. Litsea ovalifolia Lobelia nicotianifolia Macaranga indica Meliosma pinnata Michelia champaca Myristica dactyloides Neolistea fuscata Neolitsea cassia Ochlandra stridula Osbeckia lanata Pavatta indica Pongamia pinnata Strobilanthes sp. Syzygium assimile Syzygium sp. Syzygium umbrosum Trema orientale Wendlandia bicuspidata Total Plants Established Gully B - Lake Down area Common Name Gully b - Upper Lake area Scientific Name Gully a1 Upper Lake area o Planting in micro watershed 4,724 trees and plants in 39+ native and indigenous species were planted in the micro watershed of Lake Richmond. 10 8 8 4 67 76 30 25 15 97 23 103 41 10 33 75 1 6 16 7 2 5 28 40 72 62 37 33 11 12 2 7 324 8 218 308 6 3 210 1 2 13 19 1 3 0 22 444 10 510 347 2 126 18 134 3 90 161 172 216 15 40 6 53 667 93 3 19 1 6 4274 1 13 2 1 1 12 1 20 84 1 2 2 2 4 1 3 34 1 84 44 12 1 2 7 87 85 1 1 30 10 6 29 21 15 3 9 83 1 2 3 5 2 1 1 1 1 6 3 89 14 13 5 15 10 4 13 40 61 4 1 1 59 21 90 3 1 3 1 1 365 581 1 290 31 4 67 13 2 11 8 20 38 1 42 16 60 15 27 25 30 4 13 8 17 4 26 7 12 4 4 8 27 44 63 78 53 3 29 60 4 26 51 33 1 6 2 430 1193 70 62 11 58 3 97 31 121 1 170 83 6 19 2 1 150 13 1 7 1 2 690 11 63 14 1 344 11 105 5 1 381
  • 25.
  • 28. 2003 Dense planting round the well with deep rooted, native trees forming a ‘root mat ’ below the surface to uptake the contaminants.
  • 29. 0 Feb ' 4 April '04 June '4 August '04 Sept '4 October' 04 Nov '4 December' 04 Jan' 5 February'5 March'5 April'5 May'5 June'5 July'5 August'5 Sept'5 Oct'5 Nove'5 Dec'5 Jan'6 Feb'6 March'6 April'6 May'6 June'6 July'6 Aug'6 Sept'6 Oct'6 Nov'6 Dec'6 Jan'7 Feb'7 March'7 April'7 May'7 June'7 July'7 Aug'7 Sept'7 Oct'7 Nov'7 Dece'7 Jan'8 Fed'8 March'8 April'8 May'8 June'8 July ' 8 August'8 Sept'8 Oct'8 Nov'8 Dece'8 Jan'9 Concentration of N-N03 in mg/l Concentration of N-No3 over time 80 70 60 50 Lower Well 40 30 20 Upper Well 10 Concentration of Nitrate Nitrogen over time
  • 30. Electrical Conductivity at 250C over time
  • 31. References Chin, DA 2012, Water-Quality Engineering in Natural Systems : Fate and Transport Processes in the Water Environment, 2 edn, Wiley, New York. Dosskey, MG, Vidon, P, Gurwick, NP, Allan, CJ, Duval, TP & Lowrance, R 2010, 'The Role of Riparian Vegetation in Protecting and Improving Chemical Water Quality in Streams1', JAWRA Journal of the American Water Resources Association, vol. 46, no. 2, pp. 261-77. Lal, R 2004, 'Soil Carbon Sequestration Impacts on Global Climate Change and Food Security', Science, vol. 304 no. 5677 pp. 1623-7. , R & Vellidis, G 2004, 'Riparian forest buffers: hype? Or the silver bullet for NPS pollution control?', Resource: Engineering & Technology for a Sustainable World, vol. 11, no. 10, p. 7+. Melvani, K 2011, 'Bioremediation of Nitrates in Ground Water', M.Sc. thesis, University of Peradeniya Price, P. and Lovett, S. 2002, ‘Managing riparian land’, Fact Sheet 1, Land & Water Australia, Canberra