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Study of the effect of two WWTP’s discharges on benthic macroinvertebrate communities structure of the river Tinto (Portugal)

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Teresa Jesus , Álvaro Monteiro, Isabel Abreu, Maria João Guerreiro

Estudo do efeito da descarga de duas ETAR’s na estrutura

da comunidade de macroinvertebrados bentónicos do rio

Tinto (Portugal)

Study of the effect of two WWTP’s discharges on benthic

macroinvertebrate communities structure of the river

Tinto (Portugal)

The Project:

Study of the ecological status of the Tinto river

is a project proposed by LIPOR, an inter municipal company and developed by the Fernando Pessoa

University with the support of:

the four municipalities which integrates the river basin;

three water companies;

and the Portuguese Environmental Agency;

The study is carried out taking account the stablished by the WFD.

1 Km Valongo Maia Gondomar Porto

Main objectives:

Characterization of the Tinto river ecological state;

Detection of the main sources of environmental disturbance;

Preparation of proposals for measures to improve the

ecological status of the river.

(2)

Tinto river

Is a small urban watercourse in the north of Portugal belonging to the Douro river basin with about

11 km long;

Has many sources of environmental disturbance such as: channelization, waste disposal, effluent

reception of wastewater treatment plants and of untreated urban and industrial effluents.

Main objectives

 Study of some parameters related to the ecological state of Tinto river;

 Study the effect of two wastewater treatment plants (WWTPs)

discharges

on

the

structure

of

the

benthic

macroinvertebrate

communities of the Tinto River;

 Relate the composition of the macroinvertebrate communities and the

environmental conditions.

(3)

(1) (2) (3) (4) (5) (7) (8) (9) (10) (11) (13) (12) (14) (6) 0 20 40 60 80 100 120 140 160 180 200 0 0,5 1 1,5 2 2,5 3 3,5 4 4,5 5 5,5 6 6,5 7 7,5 8 8,5 9 9,5 10 10,5 11 11,5 12 H ig hn es s (m)

Distance to the source (Km) Tipology (DQA): Small Northern (N1; <= 100)

N

0,5 Km

The sampling sites

B B H H K K L L M M N N Meiral WWTP Granja creek Freixo WWTP

Methodology

Environmental parameters

➢Hydro-morphological parameters (every six months, between oct’15 and jul’17):

✓substrate composition, habitat quality, macrophytes (%), canopy (%) and flow ➢Physical and chemical parameters (every months between oct’15 and jul’17):

✓pH, conductivity, oxygen saturation, BOD5, NH4+, NO3-, NO2- , Ptotal

Benthic macroinvertebrates

➢ Sampling:

✓ With a hand net

✓Every 3 months between december’15 and july’17 (dec’15, mar’16, jun’16, sep’16, dec’16, mar’17 and jun’17)

Index and metrics:

Hydromorphological parameters:

✓ Habitat quality (AVH and QBR)

Macroinvertebrate communities:

✓Some metrics

✓Biotic indexes: RQE and IBMWP

✓Shannon´s diversity index and Pielou evenness index

✓Classification of organisms into their functional and ecological groups

➢Spatial variation of all parameters

➢N-MDS analysis of macroinvertebrates grouped according a CLUSTER analysis into functional groups and taxa and with the validation of the number of clusters by ANOSIM analysis

➢Ordination of the sampling sites made by a PCA attending the mean values of the environmental parameters and the metrics calculated with the macroinvertebrate data

Data

analysis

Parameters

5

(4)

Hydro morphological parameters

Substrate composition

0% 20% 40% 60% 80% 100% oc t'1 5 ap r'1 6 oc t'1 6 ap r'1 7 oc t'1 5 ap r'1 6 oc t'1 6 ap r'1 7 oc t'1 5 ap r'1 6 oc t'1 6 ap r'1 7 oc t'1 5 ap r'1 6 oc t'1 6 ap r'1 7 oc t'1 5 ap r'1 6 oc t'1 6 ap r'1 7 oc t'1 5 ap r'1 6 oc t'1 6 ap r'1 7

Site B Site H Site K Site L Site M Site N

Sampling sites/dates

mud silt gravel pebble cobble small blocks blocks

Dominance of material with larger diameter

Hydro morphological parameters

Macrophytes and canopy

High canopy → low urbanized areas

High percentage of macrophytes

Flow

% Sampling sites B H K L M N 0 10 20 30 40 50 60 70 80 90 % macrophytes % canopy Median 25%-75% Min-Max B H K L M N Sampling sites 0,0 0,4 0,8 1,2 1,6 2,0 2,4 2,8 Flo w (m 3/s ) Median 25%-75% Min-Max

7

(5)

Habitat Quality

Very Good

Good

Medium

Bad

Very bad

B

H

K

L

M

N

AVH

oct'15

101

130

115

129

138

128

apr'16

103

132

117

131

136

124

oct'16

78

138

115

150

155

123

apr'17

84

115

91

136

147

108

QBR

oct'15

5

20

15

30

40

45

apr'16

5

20

15

30

40

45

oct'16

0

15

0

40

45

45

apr'17

0

20

0

35

60

60

Bad and very bad quality → urban character of watercourse

Some potencial to suport aquatic life, even with some disturbance of

natural features

Hydro morphological parameters

↑ Macrophytes

↓Flow

More urbanized

areas

B H K L M N -3 -2 -1 0 1 2 3 Factor 1: 78,83% -1,5 -1,0 -0,5 0,0 0,5 1,0 1,5 Fa ct or 2: 1 7, 77 % % Macrophyte % Cannopy QBR AVH Flow -1,0 -0,5 0,0 0,5 1,0 Factor 1 : 78,83% -1,0 -0,5 0,0 0,5 1,0 Fa ct or 2 : 1 7, 77 %

↑ QBR

↑ Flow

9

(6)

WFD: % O2 between 60% and 120%;

Chemical parameters

Oxygen saturation and BOD

5

pH and Condutivity

pH Condutivity B H K L M N Sampling sites 0 1 2 3 4 5 6 7 8 9 pH 0 100 200 300 400 500 600 700 800 C on du tiv ity S/ cm)

WFD: pH: between 6 and 9 (The limits can be overcome by natural situations)

B H K L M N Sampling sites 0 10 20 30 40 50 60 70 80 90 % O 2 0 10 20 30 40 50 60 BOD 5 (mg O2 /L ) % O2 BOD5 Median 25%-75% Min-Max BOD5<= 6 mg O2/L WFD: NO3-<=25 mg NO3-/L; Median 25%-75% Min-Max

Chemical parameters

Nitrates, Nitrites and Ammonium

Total phosphorous

B H K L M N Sampling sites 0 1 2 3 4 5 To ta l P ho sp ho ro us (mg /L ) WFD: Total phosphorous: <= 0,1mg P/L A mm on iu m and N itr ite s (mg /L ) B H K L M N Sampling sites 0 20 40 60 80 100 120 140 N itr at es (mg /L ) 0 5 10 15 20 25 30 35 40 Nitrates Nitrites Ammonium NH4+<= 1 mg NH4+/L

11

(7)

Chemical parameters

B H K L N M -4 -3 -2 -1 0 1 2 3 4 Factor 1: 76,41% -1,5 -1,0 -0,5 0,0 0,5 1,0 1,5 Fa ct or 2: 1 2, 66 % pH % O2 BOD5 Nitrates Nitrites Ammonium P total -1,0 -0,5 0,0 0,5 1,0 Factor 1 : 76,41% -1,0 -0,5 0,0 0,5 1,0 Condutivity Fa ct or 2 : 1 2, 66 %

Lower degree of pollution: ↓Condutivity ↑ O2 ↓BOD 5 ↓Nutrients Some organic pollution (upstream the wwtp’s) High polluted sites

(downstream the wwtp’s): ↑ Condutivity

↓ O2

↑ BOD 5

↑ Nutrients

Macroinvertebrates: richness and abundance

0 1000 2000 3000 4000 B H K L M N N umb er of or ga ni sms Sampling sites

Richness

Abundance

0 10 20 30 40 B H K L M N N umb er of fa mil ie s Sampling sites Median 25%-75% Min-Max B H K L M N Sampling sites 0 2 4 6 8 10 N umb er of ta xa (S ) 0 500 1000 1500 2000 2500 3000 3500 4000 N nmb er of or ga ni sm s (n ) S n

13

(8)

Macroinvertebrates: diversity and equitability

0,00 0,50 1,00 1,50 2,00 B H K L M N Sh an no n’ s di ve rs ity Sampling sites 0,00 0,20 0,40 0,60 0,80 1,00 B H K L M N Pi el ou eq ui ta bi liy Sampling sites

Equitability

Diversity

B H K L M N Sampling sites 0,0 0,2 0,4 0,6 0,8 1,0 1,2 1,4 1,6 1,8 Sh an no n di ve rs ity (H ') 0,0 0,2 0,4 0,6 0,8 1,0 Pi el ou eq ui ta bi lit y (E ) Median 25%-75% Min-Max H’ P

Macroinvertebrates: EPT and Diptera taxa

0,0 0,5 1,0 1,5 2,0 2,5 B H K L M N N umb er of fa mil ie s Sampling sites 0,0 2,0 4,0 6,0 8,0 B H K L M N N umb er of fa m ili es Sampling sites

Diptera families

EPT families

Median 25%-75% Min-Max B H K L M N Sampling sites 0 1 2 3 4 5 6 7 8 N umb er of fa m ili es EPT Diptera

15

(9)

Macroinvertebrates:

% CHIRONOMIDAE & % Trichoptera

0,0 20,0 40,0 60,0 80,0 100,0 B H K L M N % of or ga ni sms Sampling sites 0,0 1,0 2,0 3,0 4,0 5,0 B H K L M N % of or ga ni sms Sampling sites

% Trichoptera

% CHIRONOMIDAE

Median 25%-75% Min-Max B H K L M N Sampling sites 0 10 20 30 40 50 60 70 80 90 % of or ga ni sms % Trichoptera % Diptera

Macroinvertebrates:

metrics

B H K L M N -5 -4 -3 -2 -1 0 1 2 3 4 Factor 1: 59,02% -3 -2 -1 0 1 2 Fa ct or 2: 2 2, 23 % abundance number of taxa Diversity Equitability EPT Diptera % CHIRONOMIDAE % Trichoptera % clingers % reophiles

% branchial and cutaneous

-1,0 -0,5 0,0 0,5 1,0 Factor 1 : 59,02% -1,0 -0,5 0,0 0,5 1,0 Fa ct or 2 : 2 2, 23 %

High polluted sites (downstream the wwtp’s): ↑ %CHIRONOMIDAE ↓EPT and Trichoptera ↓Branchial and cutaneous breathers

Lower degree of pollution: ↑ % of Trichoptera ↑ number of organisms ↑ number of taxa

Some organic pollution (upstream the wwtp’s): ↑% of CHIRONOMIDAE

↑% of clingers ↑% of reophiles

17

(10)

Macroinvertebrates:

taxa Composition

0% 20% 40% 60% 80% 100% de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7

Site B Site H Site K Site L Site M Site N

Samples (sites/dates)

Annelida e plathylelminthes Mollusca Crustacea Ephemeroptera Odonata Coleoptera Trichoptera Diptera

Communities constituted by a great amount of Annelida and Diptera with presence of

some Ephemeroptera (Baetis) and Mollusca

Downstream the WWTP there are a decrease of the Ephemeroptera and of diversitity

Macroinvertebrates:

taxa Composition

ANOSIM test: R

global

= 0,96

Taxa

Mean of each taxa in each cluster

Annelida & plathylelminthes

MolluscaCrustaceaEphemeroptera Odonata Coleoptera Trichoptera Diptera 0 10 20 30 40 50 60 70 % Cluster 1 Cluster 2 Cluster 3 Stress: 0,07

●dec’15 ●dec’16 ●mar’16 ●mar’17 ●jun’16 ●jun’17 ●sep’16 B H K L NM B H K L M N H K L M N B H K L M B H K L M N B H K L M B H K L M N N B N Cluster 2 Cluster 1 Cluster 3 Cluster 1:

• Dominance of Annelida and presence of some Ephemeroptera and Diptera

• Most of samples collected downstream the WWTP Cluster 3:

• Dominance of Diptera and presence of some Annelida and Ephemeroptera

• Include all samples collected at sites H and M (upstream each WWTP)

Cluster 2:

• Dominance of Mollusca and presence of some Ephemeroptera and Diptera

• Only samples collected at sites B and K (upstream the WWTP)

(11)

Macroinvertebrates:

breathing groups

0% 20% 40% 60% 80% 100% de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7

Site B Site H Site K Site L Site M Site N

Samples (sites/dates)

aerial branchial aerial & branchial branchial & cutaneous cutaneous pulmonar special

Communities constituted by organisms with branchial, branchial & cutaneous and special type of breathing

Dominance of special type of breathing at sites L, M and N → sites with low concentration of dissolved

oxygen

Macroinvertebrates:

breathing groups

ANOSIM test: R

global

= 0,959

B H K B H K L N B H K L M N B H K L B H K M N B H K M N B H K L M N L N M M M L N Stress: 0,07

●dec’15 ●dec’16 ●mar’16 ●mar’17 ●jun’16 ●jun’17 ●sep’16

Mean of each breathing group in each cluster

aerial branchial

aerial & branchial branchial & cutaneous

cutaneous pulmonarspecial Breathing groups 10 20 30 40 50 60 70 80 Cluster 1 Cluster 2 Cluster 3 0 % Cluster 3 Cluster 2 Cluster 1 Cluster 1:

• organisms that can survive under conditions of low oxygen concentration such as some Oligochaeta and CHIRONOMIDAE • Most of samples of sites L and N (downstream the WWTP)

Cluster 2:

• Dominance of organisms with branchial and cutaneous breathing (CHIRONOMIDAE) • Samples collected at all sites

Cluster 3:

• Dominance of organisms with pulmonar breathing (some Mollusca)

• Samples collected only at sites B and K

22

(12)

Macroinvertebrates:

feeding groups

0% 20% 40% 60% 80% 100% de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7

Site B Site H Site K Site L Site M Site N

Samples (sites/dates)

collectors limnivorous predators scrappers shredder

No great difference between the sampling sites:

• Downstream the WWTP discharges (sites L and N) there are an increase of limnivorous →

increase of organic matter on the river bed

Macroinvertebrates:

feeding groups

ANOSIM test: R

global

= 0,8

B H K M N B H KL M N B H K M N B H K L M N B H K L M B H K L M N B H K L M N L L N K Stress: 0,13

Mean of each feeding group in each cluster

colletors

limnivorouspredadors scrappers shredders

Feeding groups 0 10 20 30 40 50 60 70 % Cluster 1 Cluster 2 Cluster 3 ●dec’15 ●dec’16 ●mar’16 ●mar’17 ●jun’16 ●jun’17 ●sep’16

Cluster 3

Cluster 1

Cluster 2

Cluster 1:

• Dominance of collectors and the major diversity of feeding types • Most of samples collected at sites B, H and K (upstream the

WWTP’s) Cluster 2:

• Dominance of shredders

• Presence of collectors and limnivorous

• Sites H, M and L (at the area influenced by the WWTP) Cluster 3:

• Dominance of limnivorous

• Most of samples collected downstream the WWTP (sites L and N)

(13)

Macroinvertebrates:

habitat/locomotion preferences

0% 20% 40% 60% 80% 100% de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7

Site B Site H Site K Site L Site M Site N

Samples (sites/dates)

clingers burrowers divers swimmers sprawlers climbers

Sites L and M (downstream the WWTP) → predominance of organisms living buried in the

substrate

Other samples: clingers, swimmers and climbers

Macroinvertebrates:

habitat/locomotion preferences

ANOSIM test: R

global

= 0,879

B H K L M N B H K L M N K M N B H K L M N B H K L M N B H K L M N B H K L M N B L H

Mean of each habitat/locomotion group in each cluster

clingers

burrowersdivers swimmerssprawlers climbers

Habitat/locomotion preferences 0 10 20 30 40 50 60 70 80 % Cluster 1 Cluster 2 Cluster 3 Stress: 0,08

●dec’15 ●dec’16 ●mar’16 ●mar’17 ●jun’16 ●jun’17 ●sep’16

Cluster 1

Cluster 2

Cluster 3

Cluster 1:

• Dominance of burrowers

• Most of samples collected at sites L and N (downstream of WWTP)

Cluster 2:

• Dominance of climbers and presence of some burrowers and swimmers

• Samples of all sampling sites Cluster 3:

• The greatest diversity of organisms • Most of samples collected at sites B, H and K

(upstream of WWTP’s)

26

(14)

Macroinvertebrates:

flow preferences

0% 20% 40% 60% 80% 100% de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7

Site B Site H Site K Site L Site M Site N

Samples (sites/dates)

limnophiles most limnophiles reophiles most reophiles

Communities adapted to running water with presence of organisms that can survive in

conditions of low flow:

• According with the variability of the hydrological conditions

Macroinvertebrates:

flow preferences

ANOSIM test: R

global

= 0,857

B H K L M N B H K L M N BH L M N B H K M N B H K L M N B K M B H K L M N K H L L N Stress: 0,01

Mean of each flow preference group in each cluster

limnophiles

most limnophiles reophilesmost reophiles

Flow preferences 0 20 40 60 80 % Cluster 1 Cluster 2 Cluster 3 ●dec’15 ●dec’16 ●mar’16 ●mar’17 ●jun’16 ●jun’17 ●sep’16

Cluster 2

Cluster 3

Cluster 1

Cluster 1:

• Dominance of most limnophiles • Most of samples of sites K, L and N Cluster 2:

• Dominance of reophiles

• Samples of sites B and H (upper part of the river) Cluster 3:

• Most limnophiles and most reophiles • Samples of sites M and N

(15)

Macroinvertebrates:

IBMWP score

0% 20% 40% 60% 80% 100% de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7 de c'1 5 ma r'1 6 ju n'1 6 se p'1 6 de c'1 6 ma r'1 7 ju n'1 7

Site B Site H Site K Site L Site M Site N

Samples (sites/dates)

1 2 3 4 5 6 7 8

Communities constituted by organisms with low sensitive to pollution (score 1, 2, 3, 4 and 5)

Predominance of Oligochaeta and Diptera (CHIRONOMIDAE and SIMULIIDAE)

Presence of some BAETIDAE and Mollusca

Macroinvertebrates:

IBMWP score

ANOSIM test: R

global

= 0,831

B H K L M N B H K L M N B K L M N B L M N B H K L M N B H K L M N B K L M N H H K H Stress: 0,11 IBMWP scores ●dec’15 ●dec’16 ●mar’16 ●mar’17 ●jun’16 ●jun’17 ●sep’16

Mean of each IBMWP score in each cluster

1 2 3 4 5 6 7 8 0 10 20 30 40 50 60 70 80 90 % Cluster 1 Cluster 2 Cluster 3 Cluster 3 Cluster 1 Cluster 2 Cluster 1:

• Presence of organisms with a lower tolerance to pollution • Only samples of sites B, H and K (upstream the WWTP’s)

Cluster 2:

• Dominance of organisms with score 2 (CHIRONOMIDAE)

• Samples collected at site M, L and K Cluster 3:

• Dominance of organisms with score 1 (Oligochaeta) • All samples collected at site N

(16)

Macroinvertebrates:

biological quality

Very Good Good Medium Bad Very bad

B H K L M N IBMWP dec'15 36 29 20 11 7 12 mar'16 7 24 19 12 16 21 jun'16 16 33 19 16 15 12 sep'16 20 32 17 12 21 11 dec'16 28 15 30 23 12 7 mar'17 36 21 25 19 12 12 jun'17 27 15 21 9 8 11 EQN dec'15 0,32 0,27 0,22 0,19 0,14 0,21 mar'16 0,17 0,24 0,22 0,22 0,24 0,23 jun'16 0,23 0,28 0,35 0,23 0,21 0,18 sep'16 0,25 0,27 0,22 0,23 0,23 0,20 dec'16 0,26 0,22 0,29 0,21 0,21 0,09 mar'17 0,34 0,22 0,25 0,25 0,20 0,20 jun'17 0,27 0,22 0,22 0,10 0,13 0,30

Conclusions

After analyzing the data collected it turns out that the ecological status along the Tinto river varies

between insufficient and bad due to:

Problems on the water quality level as seems to indicate the analysis of physical-chemical

parameters and benthic macroinvertebrate communities;

Sectors of the Tinto river in which the ”natural” hydro-morphological characteristics are quite

changed (channelization, urban occupation of the banks);

The communities of macroinvertebrates are:

Poor of the taxonomic point of view and presents relatively low values of diversity;

Are dominated by organisms belonging to Annelida and Diptera with some presence of other faunal groups such as Ephemeroptera and Mollusca that are organisms that:

are adaptated the all levels of dissolved oxygen in the water;

o Collectors, shredders and limnivorous;

o prefer living buried in the substrate or in the water column (swimmer organisms)

(17)

Conclusions

The last 4 Km’s of the river are those that present a worse quality which is due to the

presence of discharges of two wastewater treatment plants that seems to increase the

pollution level of the river where it is possible to observe some features

A decrease of the oxygen concentration and an increase of organic matter in the river:

o

Higher values of nitrates, phosphorous, and fine sediments;

o

Higher values of BOD

5

and conductivity.

Communities of benthic macroinvertebrates dominated by the Oligochaeta:

o

That can survive under low oxygen conditions;

o

That live burrowed in the substrate where they can find their food and habitat.

• Flow (m3/s) Hydro morphological Conditions (average values) Macroinvertebrate Communities (average values and characterization) Physico Chemical Conditions (average values) • Canopy • Macrophytes • 0,05 • 4% • 35% • 0,3 - 0,5 • 0% - 2% • 13% - 15% • 0,6 – 1,2 • 11% - 43% • 5% - 7% •Conductivity (µS/cm) •BOD5(mg O2/L) •NH4+(mg/L) • 166 • 7,5 • 0,03 • 292 - 310 • 6,4 -9,3 • 0,95 - 1,25 • 396 - 460 • 15,4 – 17,1 • 1,3 - 2,2 •NO3-(mg/L) • 0,06 • 0,93 – 1,81 • 3,4 – 6,4 •Organisms (number) Characterisation • 13 • 10 - 11 • 6 - 7 •Taxa (number) •90

Greater diversity of taxa: • Diptera≿Oligochaeta

≿Ephemeroptera • Some times it is possible

to find some Odonata, Coleoptera and Trichoptera •790 - 1400 Communities constituted mainly by Diptera, Oligochaeta and Ephemeroptera •520 - 970 There are a dominance by Annelida but sometimes it is possible observe some Ephemroptera

Resume

Site B

Sites H, K

Sites L, M, N

(18)

The future

In order to solve the main problems founded the following works are being performed:

repair of one lifting station that causes discharges of effluents in one of the first tributaries of the

Tinto river amd which is a responsible for the decrease of qulity between sites B and H

Construction of an interceptor that will receive the effluents from the WWTP’s and that will take

them after treatment to a river with a much higher flow rate (the Douro River)

These discharges are the responsible for the great decrease of quality of rio Tinto

rehabilitation of the banks and the creation of a green corridor along most of the course of the

river

Thank you!!!

36

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