Ecological evaluation of marine macroalgal communities on five islands of Korea in the Yellow Sea
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Abstract: Macroalgae have long been used as biological indicators of marine ecosystem health worldwide due to their ecological importance and sensitivity to environmental stress. A number of previous studies have utilized macroalgal communities in monitoring surveys of environmental conditions. This study examined the characteristics and patterns of marine macroalgal communities in the Yellow Sea off the western coast of Korea. Macroalgae were analyzed for the number of species, biomass, and coverage ratio by macroalgal type. During the study period, 82 macroalgal species (10 green algae, 17 brown algae, and 55 red algae) were identified at the five study sites, with the highest number of species found at Gwanrido and Uido (both containing 41 species) and the lowest at Daeijakdo (27 species). The average biomass (via dry weight) was 98.63 g/m2, consisting of green algae (8.39 g/m2), brown algae (35.08 g/m2), and red algae (55.16 g/m2). The dominant macroalgae species in terms of biomass were Corallina pilulifera, Sargassum thunbergii, and Ulva australis in the intertidal zones, and Botryocladia wrightii and Gelidium elegans in the subtidal zones. Richness, evenness, and diversity indices based on the biomass of abundant species were 5.08, 0.65, and 2.30, respectively, over the entire study area. Based on the evaluation of the environmental states by the community indices, overall, the Ecological Evaluation Index of macroalgae communities in the study area was marked as “Good-Moderate”, but was determined as “Moderate-Low” at several sites during summer. The results can be a direct approach in the assessment of coastal habitats in which anthropogenic as well as climate change influences persist.
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Figure 2. Mean biomass (dry weight) of macroalgae in each taxonomic group across the five study sites along the western coast of Korea. a. Mean biomass combining intertidal and subtidal zones; b. mean biomass in the intertidal zone; c. mean biomass in the subtidal zone. DJD: Daeijakdo; GBD: Gyeokryeolbiyeoldo; HD: Hodo; GD: Gwanrido; UD: Uido. Error bars indicate standard deviation.
Table 1. Ecological Status Class (ESC) boundaries of transitional and coastal waters based on the Ecological Evaluation Index continuous formula (EEI-c)
ESC EEI-c (mean±SD) High (H) 9.72±0.46 Good-High (G-H) 8.09±0.74 Good-Moderate (G-M) 5.84±0.70 Moderate-Low (M-L) 4.04±0.68 Bad (B) 2.34±0.78 Table 2. Number of macroalgal species observed at the five study sites along the western coast of Korea
Site Taxon Intertidal zone Subtidal zone Total Spring Summer Spring Summer
DJDChlorophyta 2 1 2 1 3 Ochrophyta − − 4 3 5 Rhodophyta 5 6 5 13 19 Subtotal 7 7 11 17 27
GBDChlorophyta 4 − − − 4 Ochrophyta 5 2 1 1 6 Rhodophyta 12 7 8 13 25 Subtotal 21 9 9 14 35
HDChlorophyta 4 2 1 − 5 Ochrophyta 3 2 1 1 4 Rhodophyta 8 8 9 10 25 Subtotal 15 12 11 11 34
GDChlorophyta 4 4 3 1 8 Ochrophyta 5 2 4 5 11 Rhodophyta 7 5 16 8 22 Subtotal 16 11 23 14 41
UDChlorophyta 2 1 1 2 3 Ochrophyta 2 4 − 3 6 Rhodophyta 18 17 13 19 32 Subtotal 22 22 14 24 41 Note: DJD: Daeijakdo; GBD: Gyeokryeolbiyeoldo; HD: Hodo; GD: Gwanrido; UD: Uido. − represents no data. Table 3. Dominant (≥30%) and subdominant (10%−30%) species in terms of percentage of average biomass at both the intertidal zone and subtidal zone of five study sites along the western coast of Korea
Site Intertidal zone Subtidal zone DJD Ulva australis (51.41%)
Chondrus pinnulatus (13.46%)
Polyopes affinis (13.01%)Gelidium elegans (32.02%)
Chondrus pinnulatus (13.75%)GBD Gelidiophycus freshwateri (27.99%)
Corallina pilulifera (24.88%)
Chondria atropurpurea (24.67%)Botryocladia wrightii (27.44%)
Gelidium elegans (21.29%)
Rhodymenia intricata (14.49%)HD Sargassum thunbergii (48.13%)
Myelophycus simplex (12.85%)Botryocladia wrightii (22.46%)
Rhodymenia intricata (18.47%)
Gelidium elegans (14.67%)
Chondracanthus tenellus (11.37%)GD Sargassum thunbergii (66.85%) Myagropsis myagroides (23.40%)
Sargassum miyabei (22.37%)
Campylaephora hypnaeoides (13.00%)UD Corallina pilulifera (45.46%)
Ulva australis (34.63%)Gelidium vagum (57.23%)
Haraldiophyllum bonnemaisonii (12.16%)Note: DJD: Daeijakdo; GBD: Gyeokryeolbiyeoldo; HD: Hodo; GD: Gwanrido; UD: Uido. Table 4. Community indices in each intertidal and subtidal zone of five study sites in the western coast of Korea
Community indices DJD GBD HD GD UD Inter Sub Inter Sub Inter Sub Inter Sub Inter Sub Richness 2.32 3.24 3.71 3.17 3.62 2.89 2.80 4.52 5.31 5.03 Evenness 0.64 0.75 0.57 0.70 0.60 0.73 0.46 0.70 0.42 0.45 Diversity 1.59 2.33 1.85 2.04 1.91 2.06 1.39 2.35 1.44 1.53 Dominance 0.65 0.46 0.53 0.49 0.61 0.41 0.75 0.46 0.80 0.69 Note: DJD: Daeijakdo; GBD: Gyeokryeolbiyeoldo; HD: Hodo; GD: Gwanrido; UD: Uido; Inter: intertidal zone; Sub: subtidal zone. Table 5. Ecological Status Class (ESC) evaluation results of macroalgal community using Ecological Evaluation Index continuous formula (EEI-c) based on ground coverage of macroalgal species
Content DJD GBD HD GD UD Inter Sub Inter Sub Inter Sub Inter Sub Inter Sub Spring ESG I 0.00 4.80 10.43 2.10 8.70 3.40 30.18 7.05 3.88 8.54 ESG II 2.78 8.90 12.05 12.05 11.50 10.00 9.88 10.18 5.04 45.08 EEI-c 5.50 5.42 5.67 4.91 5.56 5.20 7.50 5.52 5.67 3.25 ESC G-M G-M G-M M-L G-M G-M G-H G-M G-M B EEI-c per site 5.46 5.29 5.38 6.51 4.46 ESC per site G-M G-M G-M G-M M-L Summer ESG I 2.00 16.20 3.43 2.57 5.33 1.50 5.80 11.60 7.92 11.63 ESG II 18.40 29.45 34.13 6.80 3.73 6.20 7.57 10.90 13.88 41.02 EEI-c 4.41 4.86 3.45 5.39 5.92 5.34 5.63 5.87 5.30 3.74 ESC M-L M-L M-L G-M G-M G-M G-M G-M G-M M-L EEI-c per site 4.64 4.42 5.63 5.75 4.52 ESC per site M-L M-L G-M G-M M-L Note: DJD: Daeijakdo; GBD: Gyeokryeolbiyeoldo; HD: Hodo; GD: Gwanrido; UD: Uido; Inter: intertidal zone; Sub: subtidal zone; G-H: Good-High; G-M: Good-Moderate; M-L: Moderate-Low; B: Bad. Table 6. Comparison of the number of species in each macroalgae taxonomic groups along the western sea of Korea
Tidal level Site Season Species Reference C O R Total Inter+Sub Bunjeomdoa Wi, Sp, Su, Au 9 8 37 54 Yoo and Kim (2003) Ongdoa Wi, Su 2 4 26 32 Heo et al. (2011) Jusamdob Wi, Su 4 9 32 45 Heo et al. (2011) Woejodob Wi, Su 2 6 36 44 Heo et al. (2011) Eocheongdoa Wi, Sp, Su, Au 12 23 66 101 Kim et al. (2013a) Daeijakdoa Sp, Su 3 5 19 27 this study Gyeokryeolbiyeoldoa Sp, Su 4 6 25 35 this study Hodoa Sp, Su 5 4 25 34 this study Gwanridob Sp, Su 8 11 22 41 this study Uidob Sp, Su 3 6 32 41 this study Inter Bagryoungdoa Wi, Sp, Su, Au 6 6 29 41 Baek et al. (2007) Sapsidoa Wi, Sp, Su, Au 12 30 58 100 Yoon and Boo (1991) Oeyondoa Wi, Sp, Su, Au 16 27 79 122 Cho and Boo (1996)* Sinangun UI.b Su 11 16 36 63 Oh et al. (2005) Dochogundob Su 10 14 29 53 Park et al. (2007) Deokjeokdoa Wi, Sp, Su, Au 2 2 17 21 Lee et al. (2007) Gogunsangundob Wi, Sp, Su, Au 10 16 32 58 Kim et al. (2011) Note: *Monthly basis sampling; superscripts of a and b indicate the study sites of middle and southern parts, respectively. Inter: intertidal zone; Sub: subtidal zone; Wi: winter; Sp: spring; Su: Summer; Au: Autumn; C: Chlorophyta; O: Ochrophyta (Phaeophyceae); R: Rhodophyta. -
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