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Top-down and bottom-up processes in grassland and forested streams

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Abstract

The influence of predatory fish on the structure of stream food webs may be altered by the presence of forest canopy cover, and consequent differences in allochthonous inputs and primary production. Eight sites containing introduced brown trout (Salmo trutta) and eight sites that did not were sampled in the Cass region, South Island, New Zealand. For each predator category, half the sites were located in southern beech (Nothofagus) forest patches (range of canopy cover, 65–90%) and the other half were in tussock grassland. Food resources used by two dominant herbivores-detritivores were assessed using stable isotopes. 13C/12C ratios were obtained for coarse particulate organic matter (CPOM), fine particulate organic matter (FPOM), algal dominated biofilm from rocks, and larvae of Deleatidium (Ephemeroptera) and Olinga (Trichoptera). Total abundance and biomass of macroinvertebrates did not differ between streams with and without trout, but were significantly higher at grassland sites than forested sites. However, taxon richness and species composition differed substantially between trout and no-trout sites, irrespective of whether streams were located in forest or not. Trout streams typically contained more taxa, had low biomass of predatory invertebrates and large shredders, but a high proportion of consumers with cases or shells. The standing stock of CPOM was higher at forested sites, but there was less FPOM and more algae at sites with trout, regardless of the presence or absence of forest cover. The stable carbon isotope range for biofilm on rocks was broad and encompassed the narrow CPOM and FPOM ranges. At trout sites, carbon isotope ratios of Deleatidium, the most abundant invertebrate primary consumer, were closely related to biofilm values, but no relationship was found at no-trout sites where algal biomass was much lower. These results support a role for both bottom-up and top-down processes in controlling the structure of the stream communities studied, but indicate that predatory fish and forest cover had largely independent effects.

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Acknowledgements

We thank Rennie Bishop for assistance with the field work. Lars-Anders Hansson, Anders Nilsson, Sebastian Diehl and an anonymous reviewer gave valuable comments on an earlier version of the manuscript. This study was financed by a post doctoral fellowship from Wenner-Gren foundations to P.N. and research grants from the University of Canterbury. Tracey Robinson helped prepare the manuscript.

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Correspondence to Per Nyström.

Appendix

Appendix

Abundance

Mean invertebrate abundance (individuals per m2 ±1 SE, n=4) of 58 aquatic taxa found at open and forested sites with and without trout (P predator, G grazer, F filter feeder, S shredder, N non-feeder of aquatic food sources.

Taxa

Functional Group

No trout

Trout

Open

Forest

Open

Forest

Megaloptera

Archichauliodes

P

42±25

1±1

6±4

9±5

Ephemeroptera

Austroclima

G

38±27

19±19

14±10

36±27

Coloburiscus

F

140±140

1±1

98±72

127±76

Deleatidium

G

1,107±264

646±177

1,358±261

650±77

Neozephlebia

G

0

1±1

0

1±1

Nesameletus

G

22±9

151±114

7.2±6.2

9±5

Oniscigaster

G

2±2

0

1±1

0

Plecoptera

Austroperla

S

5±5

15±13

0

5±5

Cristaperla

G

1±1

0

0

1±1

Halticoperla

G

0

0

0

1±1

Spaniocerca

G

51±50

56±32

7±6

20±6

Stenoperla

P

3±3

22±7

10±7

8±5

Taraperla

G

0

6±6

0

0

Zelandobius

G

13±5

27±16

6±2

9±3

Zelandoperla

G

1±1

5±2

0

1± 1

Trichoptera

Aoteapsyche

F

10±7

1±1

50±26

17±7

Beraeoptera

G

15±10

0

385±136

113±60

Costachorema

P

24±20

2±2

10±2

0

Edpercivalia

P

2±2

2±2

0

0

Helicopsyche

G

170±170

0

0

0

Hudsonema

G

1±1

0

0

0

Hydrobiosella

F

8±5

0

32±31

47±29

Hydrobiosis

P

3±3

11±6

8±5

8±3

Hydrochorema

P

1±1

0

2±1

4±2

Neurochorema

P

0

42±42

0

26±24

Oeconesus

S

2±2

0

0

1±1

Olinga

G

70±31

35±8

138±61

106±16

Philorheithrus

P

5±4

6±3

5±3

6±5

Polyplectropus

P

0

0

2±2

0

Psilochorema

P

3±3

0

7±5

5±4

Pycnocentria

G

0

1±1

45±43

0

Pycnocentrodes

G

0

1±1

26±13

46±28

Triplectides

S

0

0

2±2

0

Zelandopsyche

S

3±3

6±3

6±6

3±0

Zelolessica

G

1±1

0

43±21

17±7

Coleoptera

Elmidae

G

1±1

44±41

40±21

238±67

Hydraenidae

G

3±1

5±2

6±5

6±3

Hydrophilidae

G

2±2

17±7

10±7

10±4

Ptilodactylidae

G

6±6

0

0

0

Scirtidae

G

96±72

10±6

2±2

1±1

Diptera

Aphrophila

G

10±6

0

86±47

10±6

Austrosimulium

F

18±12

134±127

250±85

60±35

Chironomidae

G

172±93

34±5

377±295

73±16

Empididae

G

2±2

2±1

1±1

1±1

Eriopterini

G

2±1

2±2

3±2

4±2

Hexatomini

G

3±1

1±1

2±1

0

Muscidae

P

13±13

0

5±5

0

Nothodixa

G

0

1±1

0

0

Pelecorhynchidae

P

0

2±2

0

3±3

Tanyderidae

G

0

0

1±1

0

Mollusca

Potamopyrgus

G

146±81

10±10

64±41

55±38

Sphaerium

F

0

0

1±1

0

Platyhelminthes

Neppia

P

314±161

41±16

13±5

50±42

Nematoda

P

0

0

1±1

0

Nematomorpha

N

1±1

0

1

0

Annelida

Oligochaeta

G

46±26

38±22

58±42

29±22

Amphipoda

Paraleptamphopus

G

0

0

1±1

5±5

Acari

P

0

0

1±1

0

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Nyström, P., McIntosh, A.R. & Winterbourn, M.J. Top-down and bottom-up processes in grassland and forested streams. Oecologia 136, 596–608 (2003). https://doi.org/10.1007/s00442-003-1297-1

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