Stream restoration in the Netherlands – two examples ... · Stream restoration in the Netherlands...

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Stream restoration in the Netherlands Stream restoration in the Netherlands ––

two examples differing in scaletwo examples differing in scale

Roos LoebKarin DidderenPiet Verdonschot

Contents

� National survey on stream restoration

� Small-scale restoration: woody debris in the Jufferbeek

� Large-scale-project: restoration of the Geeserstroom

� Conclusions

Stream restoration survey – where?

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upper course

middle course

lower course

upper&middle course

upper to lower c

ourse

middle&lower course

restoration projects per stream course

% o

f p

roje

cts

Stream restoration survey – measures

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remeander(active)

reprofile raise drainagebase

raisegroundwater level

developinundation zone

increase waterretetion/storage

hydrology & morphology

01020304050607080

low gradientbanks

fish migrationpaths

asymetricalprofile

plant wood onbanks

stream and bank arrangement

01020304050607080

change landuse

top soilremoval

buffer zones reduce inflowcontaminants

water quality

% o

f p

roje

cts

% o

f p

roje

cts

% o

f p

roje

cts

Stream restoration inquiry – monitoring

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hydrology

morphology

water quality fish

macrophytes

bank vegetation

macro!invertebrates

phytobenthos

unknownnothing

monitoring both before and after

restoration

Wood experiment in the Jufferbeek

� Free-flowing discharge� Removal of leaves and branches� 1-5% coverage of organic matter (naturally 25% wood, 25%

leaves)

� Effects� Habitat disappearance for stream-dwelling organisms� Homogeneity of habitats� Increased discharge� Bed-incisions and drought

� Wood addition could be a cheap restoration measure for a small part of a stream course

� Jufferbeek: upper course in the east of the Netherlands� 2 locations: upstream (control) and section with wood

addition (300 m)� Spring 2006: wood was added to a coverage 25%

wood section

control section

Wood experiment in the Jufferbeek

0%

10%20%

30%40%

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60%70%

80%90%

100%

Apr-05

Oct-05

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Nov-07

c o n t r o l w o o d s e c t

cove

rag

e

fdetri cdetri silt leaves veg wood bran sand

Wood experiment in the Jufferbeek

finedetritus

coarsedetritus

silttwigsleavesvegetationsandfine gravel

flo

wve

loci

ty(m

/s)

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0,00 a b c dc c d e

Wood experiment

�2

�1.5�1

�0.50

0.51

1.52

2.53

E uk ie ffe rie lla c la r ip enn isN eo lim nom y ia spM id eop s is c ra ss ip esT ub ifex tu b ifexL accob iu s b ip un c ta tu sL im nod rilu s h o ffm e is te riC h ry sop ilu s spL eb ertia in aequ a lisT ub ific id aeN ep a c in e reaA u lod rilu s japon icu sP rod iam esa o livaceaV e lia c ap ra iP o tam o th rix b edo tiL eb ertia lin ea taN eum an ia v e rn a lisH yd ro chu s spP o lyp ed ilum sca la en umO ph id ona is se rp en tin aE lod es spL im nod rilu s p ro fund ico laA eshn a spM ic rop te rn a la te ra lisC e ra top ogon id aeS tagn ico la spB a th yom pha lu s con to rtu sH ippeu tis com p lan a tu sH yg ro tu s in aequ a lisH e loph o ru s a eq u a lisM o loph ilu s spN eph ro tom a spZ avre lie lla spC o ryn on eu ra c f an ten n a lisT aban id aeP lec tro cn em ia con sp e rsaG yrau lu s spB e raeod es m inu tu sS tem pe llin a spSpe rchon th ien em ann iG am m aru s p u lexB ae tis v e rn u sS egm en tin a n it id aA rrenu ru s c y lin d ra tu sC lado tan y ta rsu s spR ad ix o va taZ avre lim y ia spA n acaen a spS ia lis lu ta riaC lo eon d ip te rumP isid ium spG a lb a trun ca tu laP ro c lad iu s spP roa se llu s m e rid ian u s

taxon gewicht

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before after

nu

mb

ero

f m

acro

inve

rteb

rate

tax

a control

wood section

Taxon increase

Large-scale restoration: Geeserstroom

Before� Deeply incised, canalized, short length, limited slope� Eutrophication from agriculture and sewer overflow� No fish migration possible (weirs)

Large-scale restoration: Geeserstroom

Restoration measures� New, meandering stream bed (2005)� Close-off + diversion agricultural waters� Only 1 weir with fish ladder

Historical situation

Large-scale restoration: Geeserstroom

Historical situation

Large-scale restoration: Geeserstroom

110115max water depth (cm)

2770average water depth (cm)

8512max width (m)

97average width (m)

2110slope (%)

8.96.0distance to fish ladder (km)

after restorationbeforerestoration

Large-scale restoration: Geeserstroom

Roonboomdijk

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0.05

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0.15

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0.25

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0.45

Jan-

05

Apr-0

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Jul-0

5

Oct-05

Jan-

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Oct-07

conc

entr

atio

nph

osph

orus

(mg

P/l)

DIP

DOP

Large-scale restoration: Geeserstroom

Roonboomdijk

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atio

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Large-scale restoration: Geeserstroom

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µ

m

� 3 common, (hyper) eutrophic taxa dominant (pioneer species)

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m

Cocconeis placentula Achnanthidium minutissimum Gomphonema parvulum

Large-scale restoration: Geeserstroom

Diatoms

macroinvertebrates(dis)appearance

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10

Hyd

raca

rina

Biv

alvi

a

Hiru

dine

a

Am

phip

oda

Meg

alop

tera

Odo

nata

Olig

ocha

eta

Tric

hopt

era

Gas

trop

oda

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eopt

era

Bra

chyc

era

Eph

emer

opte

ra

Isop

oda

Lepi

dopt

era

Pla

tyhe

lmin

thes

Nem

atoc

era

Chi

rono

mid

ae

Het

erop

tera

Rat

io a

ppea

red/

disa

ppea

red

taxa

Large-scale restoration: Geeserstroom

Index for rheophilic species Index for drought tolerant species

n.s.

Large-scale restoration: Geeserstroommacroinvertebrates

*

Conclusions

� Dispersion plays an important role in (re)colonisation; flying species reach restored stream more easily than non-flying species

� (Re)colonisation and vegetation development take time: long-term monitoring necessary

� Exceeding nutrient norms may hamper development of ecology

Conclusions

� Many projects in the Netherlands only focus on a small section of a stream, no restoration of entire catchments (+ problems from upstream sections)

� Most effort put into hydrological and morphological changes, little into nutrients

� Many projects are not monitored (especially not for biological targets). A before-after-control-impact monitoring would be best.

� Need for scientific research to gain do’s and don’ts in lowland stream restoration