Figure 1

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Figure 5

Figure 6

Number of benthic macroinvertebrate individuals per m2 in different seasons
| Benthic macroinvertebrates | Seasons | ||||
|---|---|---|---|---|---|
| Spring | Summer | Autumn | Average | ||
| Oligochaeta GROUP | Henlea perpusilla | 133 | 0 | 0 | 44 |
| Lumbriculus variegatus | 0 | 0 | 178 | 59 | |
| Stylodrilus heringianus | 0 | 211 | 33 | 82 | |
| Eiseniella tetraedra | 6 | 11 | 28 | 15 | |
| Aulophorus furcatus | 0 | 0 | 28 | 9 | |
| Chaetogaster limnaei | 0 | 0 | 100 | 33 | |
| Dero digitata | 0 | 28 | 0 | 9 | |
| Pristina longiseta | 0 | 11 | 22 | 11 | |
| Limnodrilus hoffmeisteri | 0 | 694 | 150 | 281 | |
| Limnodrilus sp. | 0 | 0 | 283 | 95 | |
| Tubifex tubifex | 0 | 78 | 211 | 97 | |
| Oligochaeta (unidentified) | 56 | 0 | 400 | 152 | |
| Chironomidae GROUP | Tanypus punctipennis | 0 | 0 | 56 | 18 |
| Halocladius fucicola | 0 | 156 | 0 | 52 | |
| Chironomus plumosus | 161 | 1983 | 44 | 729 | |
| Chironomus tentans | 0 | 4178 | 0 | 1393 | |
| Cladotanytarsus defectus | 0 | 83 | 22 | 35 | |
| Kiefferulus tendipediformis | 0 | 6 | 0 | 2 | |
| Polypedilum convictum | 0 | 0 | 428 | 143 | |
| Polypedilum nubifer | 44 | 2361 | 2711 | 1706 | |
| Cladotanytarsus mancus | 28 | 0 | 0 | 9 | |
| Virgatanytarsus arduennensis | 0 | 150 | 0 | 50 | |
| Chironomidae (unidentified) | 0 | 183 | 0 | 61 | |
| Other Insecta GROUP | Cloeon dipterum | 11 | 33 | 222 | 89 |
| Ischnura elegans | 0 | 6 | 28 | 11 | |
| Orthetrum albistylum | 0 | 0 | 33 | 11 | |
| Sigara lateralis | 11 | 11 | 11 | 11 | |
| Sigara striata | 0 | 0 | 83 | 27 | |
| Corixidae (nymph) | 0 | 206 | 0 | 69 | |
| Hydroglyphus geminus | 0 | 267 | 4711 | 1659 | |
| Peltodytes caesus | 72 | 0 | 0 | 24 | |
| Berosus spinosus | 17 | 0 | 0 | 6 | |
| Coleoptera ( larvae) | 100 | 117 | 33 | 83 | |
| Ceratopogonidae | 6 | 0 | 11 | 6 | |
| Culicidae | 0 | 6 | 356 | 120 | |
| Ephydridae | 0 | 44 | 22 | 22 | |
| Stratiomyidae | 0 | 33 | 44 | 26 | |
| Other Taxa GROUP | Nematoda | 567 | 1411 | 161 | 713 |
| Erpobdella octoculata | 0 | 22 | 11 | 11 | |
| Physella acuta | 61 | 306 | 178 | 182 | |
| Gyraulus piscinarum | 0 | 28 | 11 | 13 | |
| Planorbis carinatus | 0 | 189 | 0 | 63 | |
| Planorbis sp. | 111 | 33 | 67 | 70 | |
| Ostracoda | 122 | 1378 | 0 | 500 | |
| Hydrachnidae | 0 | 61 | 6 | 22 | |
| Diplostraca | 0 | 0 | 383 | 128 | |
| Gammarus komareki | 0 | 6 | 0 | 2 | |
| Total Oligochaeta | 195 | 1033 | 1433 | 887 | |
| Total Chironomidae | 233 | 9100 | 3261 | 4198 | |
| Total Other Insecta | 217 | 723 | 5554 | 2164 | |
| Total Other Taxa | 861 | 3434 | 817 | 1704 | |
| Total | 1506 | 14290 | 11065 | 8953 | |
| Number of taxa | 16 | 32 | 33 | 47 | |
Hypothesis effect matrix and relative values
| Pressure elements | Criteria | |||
|---|---|---|---|---|
| Oligochaeta | Chironomidae | Other Insecta | Other taxa | |
| Heavy metals (S1) | 2 | 2 | 1 | 1 |
| Nutrients (S2) | 2 | 1 | 1 | 1 |
| Other physicochemical parameters (S3) | 1 | 1 | 1 | 1 |
| Pesticides (S4) | 3 | 3 | 2 | 1 |
The scale used to represent the risk factors of Eir, Ri, ERM-Qi and mERM-Q (Long et al_ 2005)
| Potential Ecological Risk Assessment | Biological Risk Assessment | ||||
|---|---|---|---|---|---|
| Eir | Potential ecological risk for monomial factors | RI | Potential ecological risk for multinomial factors | ERM-Qi and mERM-Q | Biological toxicity risk for monomial and multinomial factors |
| < 40 | low ecological risk | < 95 | low ecological risk | < 0.1 | low priority side |
| 40–80 | moderate ecological risk | 95–190 | moderate ecological risk | 0.1–0.5 | medium-low priority side |
| 80–160 | considerable ecological risk | 190–380 | considerable ecological risk | 0.5–1.5 | high-medium priority side |
| 160–320 | high ecological risk | > 380 | very high ecological risk | > 1.5 | high priority side |
| > 320 | very high ecological risk | ||||
Abundance of benthic macroinvertebrate species per m2 at the sampling locations (Ave – average, Abd – abundance, TA – total abundance)
| Macroinvertebrates | Sampling locations | |||||||
|---|---|---|---|---|---|---|---|---|
| A | M | E | ME | ME | Ave | Abd | TA | |
| Oligochaeta GROUP | Henlea perpusilla | 66 | 14 | 0 | 96 | 44 | 5 | 0.5 |
| Lumbriculus variegatus | 0 | 0 | 0 | 236 | 59 | 6.7 | 0.7 | |
| Stylodrilus heringianus | 0 | 246 | 0 | 82 | 82 | 9.2 | 0.9 | |
| Eiseniella tetraedra | 44 | 0 | 0 | 14 | 15 | 1.6 | 0.2 | |
| Aulophorus furcatus | 36 | 0 | 0 | 0 | 9 | 1 | 0.1 | |
| Chaetogaster limnaei | 134 | 0 | 0 | 0 | 34 | 3.8 | 0.4 | |
| Dero digitata | 38 | 0 | 0 | 0 | 9 | 1.1 | 0.1 | |
| Pristina longiseta | 14 | 0 | 0 | 30 | 11 | 1.2 | 0.1 | |
| Limnodrilus hoffmeisteri | 1104 | 22 | 0 | 0 | 281 | 31.8 | 3.1 | |
| Limnodrilus sp. | 378 | 0 | 0 | 0 | 94 | 10.7 | 1.1 | |
| Tubifex tubifex | 0 | 104 | 0 | 282 | 96 | 10.9 | 1.1 | |
| Oligochaeta (unidentified) | 548 | 0 | 0 | 58 | 152 | 17.1 | 1.7 | |
| Chironomidae GROUP | Tanypus punctipennis | 0 | 0 | 74 | 0 | 19 | 0.4 | 0.2 |
| Halocladius fucicola | 0 | 208 | 0 | 0 | 52 | 1.2 | 0.6 | |
| Chironomus plumosus | 60 | 408 | 296 | 2154 | 730 | 17.4 | 8.1 | |
| Chironomus tentans | 0 | 0 | 5570 | 0 | 1393 | 33.2 | 15.6 | |
| Cryptochironomus defectus | 0 | 110 | 0 | 30 | 35 | 0.8 | 0.4 | |
| Kiefferulus tendipediformis | 0 | 6 | 0 | 0 | 2 | 0.1 | 0.1 | |
| Polypedilum convictum | 0 | 0 | 572 | 0 | 143 | 3.4 | 1.6 | |
| Polypedilum nubifer | 192 | 1926 | 4170 | 534 | 1705 | 40.6 | 19.1 | |
| Cladotanytarsus mancus | 0 | 38 | 0 | 0 | 9 | 0.2 | 0.1 | |
| Virgatanytarsus arduennensis | 90 | 112 | 0 | 0 | 50 | 1.2 | 0.6 | |
| Chironomidae (unidentified) | 244 | 0 | 0 | 0 | 61 | 1.5 | 0.7 | |
| Other Taxa GROUP | Cloeon dipterum | 14 | 58 | 266 | 14 | 88 | 4.1 | 1 |
| Ischnura elegans | 0 | 8 | 28 | 8 | 11 | 0.5 | 0.1 | |
| Orthetrum albistylum | 0 | 8 | 38 | 0 | 11 | 0.5 | 0.1 | |
| Sigara lateralis | 0 | 0 | 44 | 0 | 11 | 0.5 | 0.1 | |
| Sigara striata | 0 | 0 | 112 | 0 | 28 | 1.3 | 0.3 | |
| Corixidae (nymph) | 8 | 214 | 28 | 22 | 68 | 3.1 | 0.8 | |
| Hydroglyphus geminus | 4414 | 222 | 1978 | 22 | 1659 | 76.7 | 18.5 | |
| Peltodytes caesus | 0 | 0 | 0 | 96 | 24 | 1.1 | 0.3 | |
| Berosus spinosus | 22 | 0 | 0 | 0 | 5 | 0.3 | 0.1 | |
| Coleoptera ( larvae) | 30 | 52 | 112 | 140 | 84 | 3.9 | 0.9 | |
| Ceratopogonidae | 8 | 0 | 8 | 8 | 6 | 0.3 | 0.1 | |
| Culicidae | 8 | 0 | 466 | 8 | 121 | 5.6 | 1.3 | |
| Ephydridae | 22 | 0 | 66 | 0 | 22 | 1 | 0.2 | |
| Stratiomyidae | 28 | 0 | 22 | 52 | 26 | 1.2 | 0.3 | |
| Other Taxa GROUP | Nematoda | 1504 | 282 | 556 | 512 | 713 | 41.9 | 8 |
| Erpobdella octoculata | 8 | 8 | 28 | 0 | 11 | 0.6 | 0.1 | |
| Physella acuta | 206 | 52 | 186 | 282 | 182 | 10.7 | 2 | |
| Gyraulus piscinarum | 0 | 0 | 14 | 38 | 13 | 0.8 | 0.1 | |
| Planorbis carinatus | 0 | 8 | 0 | 244 | 63 | 3.7 | 0.7 | |
| Planorbis sp. | 44 | 88 | 0 | 148 | 70 | 4.1 | 0,8 | |
| Ostracoda | 1874 | 126 | 0 | 0 | 500 | 29.3 | 5.6 | |
| Hydrachnidae | 0 | 44 | 8 | 36 | 22 | 1.3 | 0.2 | |
| Diplostraca | 0 | 0 | 512 | 0 | 128 | 7.5 | 1.4 | |
| Gammarus komareki | 8 | 0 | 0 | 0 | 2 | 0.1 | 0 | |
| Oligochaeta Total | 2362 | 386 | 0 | 798 | 886 | 100 | 9,9 | |
| Chironomidae Total | 586 | 2808 | 10682 | 2718 | 4199 | 100 | 46,9 | |
| Other Insecta Total | 4554 | 562 | 3168 | 370 | 2164 | 100 | 24,2 | |
| Other Taxa Total | 3644 | 608 | 1304 | 1260 | 1704 | 100 | 19 | |
| Total | 11146 | 4364 | 15154 | 5146 | 8953 | 100 | 100 | |
| Number of taxa | 28 | 24 | 23 | 25 | 47 | |||
Concentrations of the determined pesticides in water samples (ppm)
| Pesticide | Station | |||
|---|---|---|---|---|
| Artesian | Meriç | Ergene | Meriç-Ergene | |
| Acetamiprid | 0.0227 | 0.0497 | 1.2092 | 0.672 |
| Azoxystrobin | 0.0401 | 1.0789 | 13.6247 | 0.2291 |
| Carbendazim | 0.374 | 1.8176 | 2.163 | 0.9806 |
| Carbofuran | 0.0069 | 0.0105 | * | * |
| Cyproconazole | * | * | 12.3969 | * |
| Dicrotophos | * | 0.0122 | * | 0.0097 |
| Dimoxystrobin-688 | 0.0416 | * | * | 0.0488 |
| Ethiofencarb | * | 0.0549 | 0.0734 | 0.0677 |
| Fluoxastrobin-698 | 0.0749 | 0.2242 | 0.1022 | 0.0803 |
| Flutriafol | 0.1847 | 0.1777 | 0.2103 | 0.1871 |
| Forchlorfenuron-706 | 0.6974 | 1.3388 | 1.1613 | 2.4202 |
| Mandipropamid | * | * | * | 0.0703 |
| Monocrotophos | 0.0062 | 0.0102 | * | 0.0098 |
| Pirimicarb | 0.0097 | 0.01 | 0.0052 | 0.0066 |
| Prometryn | 0.021 | * | * | * |
| Spiroxamine | * | 0.0546 | * | 0.0721 |
| Tebuthiuron | 0.0204 | 0.0113 | 0.0228 | 0.0206 |
| Thiabendazole | 0.0402 | 0.0353 | 0.0276 | 0.0228 |
| Thiacloprid | 0.0229 | 0.025 | 0.026 | 0.0273 |
| Trifloxystrobin | 0.1061 | 0.1048 | 0.1055 | 0.0507 |
| Vamidathion | 0.0051 | 0.0087 | 0.0036 | 0.0077 |
| Number of pesticides | 16 kinds | 17 kinds | 15 kinds | 18 kinds |
Results of the potential ecological risk index associated with the presence of heavy metals measured in sediment at sampling sites
| Water resources | Eir | RI | |||
|---|---|---|---|---|---|
| Cd | Cu | Ni | Mn | ||
| Artesian | 26.826 | 0.610 | 0.139 | 0.016 | 27.591 |
| Meriç River | 49.125 | 1.233 | 0.078 | 0.015 | 50.451 |
| Ergene River | 25.215 | 0.458 | 0.122 | 0.017 | 25.811 |
| Meriç-Ergene mixed | 32.280 | 0.476 | 0.086 | 0.016 | 32.857 |
Results of the hypothetical impact matrix
| Stressors assessment | S1 | S2 | S3 | S4 | Row sum |
|---|---|---|---|---|---|
| (impact assessment) | |||||
| S1 | 0 | 1 | 2 | –3 | 0 |
| S2 | –1 | 0 | 1 | –4 | –4 |
| S3 | –2 | –1 | 0 | –5 | –8 |
| S4 | 3 | 4 | 5 | 0 | 12 |
Sampling locations
| Sampling location | Location of paddy fields | Irrigation water source | Coordinates |
|---|---|---|---|
| A1 | Havsa (Necatiye village) | Artesian water | 41°30’20”N; 26°53’28”E |
| A2* | Tekirdağ (Hayrabolu) | Artesian water | 41°13’05”N; 27°06’58”E |
| M1 | Meriç (Küplü village) | Meriç River | 41°02’10”N; 26°20’36”E |
| M2* | Edirne (Kapikule) | Meriç River | 41°42’37”N; 26°22’31”E |
| E1 | Uzunköprü (Çiftlik village) | Ergene River | 41°14’27”N; 26°37’02”E |
| E2* | Uzunköprü (Centrum) | Ergene River | 41°15’46”N; 26°41’32”E |
| ME1 | Ipsala (Border Gate) | Meriç + Ergene River | 40°55’47”N; 26°20’50”E |
| ME2* | Ipsala (Yenikarpuzlu village) | Meriç + Ergene River | 40°46’38”N; 26°17’08”E |
Biological risk index results for sediments at the sampling locations
| Water resources | ERM-Qi | |||
|---|---|---|---|---|
| Cd | Cu | Ni | mERM-Qi | |
| Artesian | 0.049 | 0.009 | 0.02 | 0.026 |
| Meriç River | 0.09 | 0.018 | 0.01 | 0.039 |
| Ergene River | 0.046 | 0.007 | 0.02 | 0.024 |
| Meriç-Ergene mixed | 0.059 | 0.007 | 0.01 | 0.025 |
Reference values for the analyzed heavy metals (Cin), toxicity coefficient (Tir), medium effect range (ERM) (Hakanson 1980; Xu et al_ 2008)
| Element | RI | mERM-Q | |
|---|---|---|---|
| Cin | Tir | ERM | |
| Cd | 0.5 | 30 | 9 |
| Cu | 30 | 5 | 390 |
| Ni | 50 | 5 | 50 |
| Mn | 860 | 1 | - |
Concentration of heavy metals in sediment samples (ppm)
| Water resources | Heavy metals | |||
|---|---|---|---|---|
| Cd | Ni | Cu | Mn | |
| Artesian | 0.441 | 1.388 | 3.659 | 13.722 |
| Meriç River | 0.818 | 0.78 | 7.397 | 13.169 |
| Ergene River | 0.42 | 1.217 | 2.748 | 14.405 |
| Meriç–Ergene rivers (mixed) | 0.538 | 0.858 | 2.855 | 13.485 |
Physicochemical parameters at the sampling locations in the study season
| Unit | Spring | Summer | Autumn | Average | Standard Deviation | Water quality | |
|---|---|---|---|---|---|---|---|
| Temperature | °C | 26.3 | 30.9 | 20.5 | 25.9 | ± 5.2 | II |
| pH | 8.8 | 7.6 | 5.8 | 7.4 | ± 1.5 | I | |
| Conductivity | μS cm-1 | 813.5 | 1707.5 | 2437.1 | 1652.7 | ± 813.2 | III |
| Salinity | ‰ | 0.5 | 0.8 | 1.3 | 0.9 | ± 0.4 | - |
| TDS 500 | 500 | 1100 | 1400 | 1000 | ± 458.2 | I | |
| Ca+2 | mg l-1 | 53.3 | 33.2 | 57.9 | 48.1 | ± 13.1 | - |
| Mg+2 | 6.1 | 4.2 | 0.0 | 3.4 | ± 3.1 | - | |
| T.H. | FS | 18.9 | 7.6 | 38.5 | 21.7 | ± 15.6 | - |
| NO2-N | 0.1 | 0.0 | 0.0 | 0.0 | ± 0.1 | I | |
| NO3-N | 4.5 | 2.6 | 1.8 | 3 | ± 1.4 | I | |
| PO4-3 | mg l-1 | 0.3 | 0.3 | 0.2 | 0.3 | ± 0.1 | II |
| SO4-2 | 3.6 | 3.1 | 2.7 | 3.1 | ± 0.5 | I | |
| D.O. | 4 | 5.6 | 3.5 | 4.4 | ± 1.1 | III |