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Bart Reeze, RIZA Biological Invasions in Inland Waters Invasive macroinvertebrates and the ecological quality of large rivers B. Reeze, M. Greijdanus, A. bij de Vaate RIZA (The Netherlands)

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  • Bart Reeze, RIZA

    Biological Invasions in Inland Waters

    Invasive macroinvertebrates and the ecological quality of large rivers

    B. Reeze, M. Greijdanus, A. bij de Vaate RIZA (The Netherlands)

  • Bart Reeze, RIZABiological Invasions in Inland Waters 2

    Invasions: where’s the party?5th May: liberation day

  • Bart Reeze, RIZABiological Invasions in Inland Waters 3

    Contents

    • observations in river Rhine and Meuse• assessment macro-invertebrates European

    Water Framework Directive (WFD)• discussion: how to deal with invasive

    species?

  • Bart Reeze, RIZABiological Invasions in Inland Waters 4

    River Rhine and Meuse

  • Bart Reeze, RIZABiological Invasions in Inland Waters 5

    Invasions river Rhine

    Abundance invasive species Lobith

    0%10%20%30%40%50%60%70%80%90%

    100%

    1988 1989 1990 19911992 1993 1994 1995 1996 1997 1998 19992000 2001 2002 2003

    rela

    tive

    abun

    danc

    e

    010.00020.00030.00040.00050.00060.00070.00080.00090.000100.000

    abun

    danc

    e

    nativeother invasiveC. curvispinumG. tigrinusJ. istriD. polymorphaD. villosusabundance

  • Bart Reeze, RIZABiological Invasions in Inland Waters 6

    Invasions river Meuse

    Abundance invasive species Grave

    0%10%20%30%40%50%60%70%80%90%

    100%

    1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003

    rela

    tive

    abun

    danc

    e

    0

    5.000

    10.000

    15.000

    20.000

    25.000

    30.000

    35.000

    40.000

    abun

    danc

    e

    nativeother invasiveC. curvispinumG. tigrinus

    J. istriD. polymorphaD. villosusabundance

  • Bart Reeze, RIZABiological Invasions in Inland Waters 7

    Invasions: main stream vs. secundary channels

    Presence and abundance of invasive speciesmain stream vs. secundary channels

    0

    20

    40

    60

    80

    100

    species individuals

    %

    main streamsecundary channels

  • Bart Reeze, RIZABiological Invasions in Inland Waters 8

    Invasions observations

    • mainly on hard substratum, up to 50% abundance on bottom substrates

    • few species (25%) cover > 90% of abundance

    • succession dominant species• mainly large rivers and lakes (till so far?)• hypothesis: habitat-diversity favours native

    species

  • Bart Reeze, RIZABiological Invasions in Inland Waters 9

    Ecological quality: EuropeanWater Framework Directive

    Benthic invertebrates = quality elementClassification waterbodies in 5 classes:• composition and abundance• deviance from type-specific communitites

    (reference conditions)

  • Bart Reeze, RIZABiological Invasions in Inland Waters 10Assessment of

    macroinvertebrates in the Netherlands

    List of characteristic taxa (KM), dominant positive (DP) and dominant negative (DN) taxa per type

    Classification based on 3 metrics:• negative dominant species (DN%, abundance)• characteristic species (KM%, taxa)• positive dominant and characteristic species (DP%+KM%,

    abundance)

    Recently (< 10 years) introduced invasive species do not belong to taxa lists

  • Bart Reeze, RIZABiological Invasions in Inland Waters 11

    Example

    1 Calculate form species-list:• % dominant negative taxa (DN%, abundance)• % characteristic taxa (KM%, taxa)• % dominant positive and characteristic taxa (KM%+DP%, abundance)

    metric value score DN % (abundance) ≥ 41 0,1 < 41 0,2 KM % (nr taxa) ≤ 7 0,1 > 7 - ≤ 17 0,2 > 17 - ≤ 32 0,3 > 32 0,5 KM %+DP % (abundance) < 5 0,1 ≥ 5 - < 25 0,2 ≥ 25 0,3

    2metric value score DN % (abundance) ≥ 41 0,1 < 41 0,2 KM % (nr taxa) ≤ 7 0,1 > 7 - ≤ 17 0,2 > 17 - ≤ 32 0,3 > 32 0,5 KM %+DP % (abundance) < 5 0,1 ≥ 5 - < 25 0,2 ≥ 25 0,3

    2

    total score class ≤ 0,3 bad

    > 0,3 - < 0,6 poor ≥ 0,6 - < 0,8 moderate ≥ 0,8 – ≤ 0,9 good > 0,9 – ≤ 1,0 high

    3total score class ≤ 0,3 bad

    > 0,3 - < 0,6 poor ≥ 0,6 - < 0,8 moderate ≥ 0,8 – ≤ 0,9 good > 0,9 – ≤ 1,0 high

    3

  • Bart Reeze, RIZABiological Invasions in Inland Waters 12

    Impact of invasive species

    Invasive species have an effect on the assessment results:

    • by their high relative abundance• by diminishing the chance of being found for

    other (characteristic) species

  • Bart Reeze, RIZABiological Invasions in Inland Waters 13

    Impact of invasive species: groups

    R7 R8 R16

    no impact, densities too lowDendrocoelum romanodanubiale Turbellaria 0 0 0Caspiobdella fadejewi Hirudinea 0 0 0Atyaephyra desmaresti Crustacea 0 0 0Orconectes limosus Crustacea 0 0 0Hemimysis anomala Crustacea 0 0 0Menetus dilatatus Mollusca 0 0 0

    negative impact, high abundanceCorophium curvispinum Crustacea -- -- --Hypania invalida Polychaeta - - -

    negative or positive impact, competitionEchinogammarus ischnus Crustacea -- - -Proasellus meridianus Crustacea + + -Proasellus coxalis Crustacea + + -Jaera istri Crustacea + + -

    species is part of assessmentHydropsyche bulgaromanorum Trichoptera 0 - -Potamopyrgus antipodarum Mollusca 0 - 0Gammarus tigrinus Crustacea -- + -Gammarus roeselii Crustacea + 0 0Nanocladius rectinervis Chironomidae 0 0 +Rheocricotopus chalybeatus Chironomidae 0 0 +Dreissena polymorpha Mollusca + + +Corbicula fluminea Mollusca + ++ +

    othersDikerogammarus villosus Crustacea ? ? ?Corbicula fluminalis Mollusca + + +Ferrissia wautieri Mollusca - 0 -

    watertype

  • Bart Reeze, RIZABiological Invasions in Inland Waters 14

    How to deal with invasive species in ecological quality assessments?

    • exclude invasive species (assessment based on native species only)

    • transform current metrics for log-transformed data (to diminish effect of invasive species)

    • assign invasive species as %DN, %KM or %DP depending on their impact

    • exclude biotopes (mainly hard substrates) from the assessment procedure

    • connect reliability of assessment to (new) metric indicating the impact of invasive species

    • introduce a metric based on other characteristics (i.e. diversity, functional groups)