{"title":"不同红树林地点营养物、生物量和细菌数量的测定:营养物依赖生物量生产的比较研究","authors":"Sadar Aslam, You-Shao Wang","doi":"10.1002/ece3.71697","DOIUrl":null,"url":null,"abstract":"<p>This study was conducted at eight different sites of the mangrove ecosystem in Kaozhou Yang, Huidong District, Huizhou Guangdong, South China Sea. The concentration of nutrients (<span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NH</mi>\n <mn>4</mn>\n <mo>+</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NH}}_4^{+} $$</annotation>\n </semantics></math>, <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NO</mi>\n <mn>2</mn>\n <mo>−</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NO}}_2^{-} $$</annotation>\n </semantics></math>, <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NO</mi>\n <mn>3</mn>\n <mo>−</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NO}}_3^{-} $$</annotation>\n </semantics></math>, <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>PO</mi>\n <mn>4</mn>\n <mrow>\n <mn>3</mn>\n <mo>−</mo>\n </mrow>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{PO}}_4^{3-} $$</annotation>\n </semantics></math> and <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>SiO</mi>\n <mn>3</mn>\n <mrow>\n <mn>2</mn>\n <mo>−</mo>\n </mrow>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{SiO}}_3^{2-} $$</annotation>\n </semantics></math>) was determined (both water and soil samples). Based on the nutrient concentration, the comparison of mangrove biomass production, total organic matter and bacterial count were also investigated. The level of nutrient values and biomass production of mangrove and bacterial count in both water and soil samples followed the same trend. The results showed that the highest concentration of <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NH</mi>\n <mn>4</mn>\n <mo>+</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NH}}_4^{+} $$</annotation>\n </semantics></math> (0.457 ± 0.051 mg/L), <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NO</mi>\n <mn>2</mn>\n <mo>−</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NO}}_2^{-} $$</annotation>\n </semantics></math> (0.223 ± 0.018 mg/L), <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NO</mi>\n <mn>3</mn>\n <mo>−</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NO}}_3^{-} $$</annotation>\n </semantics></math> (0.521 ± 0.038 mg/L), <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>PO</mi>\n <mn>4</mn>\n <mrow>\n <mn>3</mn>\n <mo>−</mo>\n </mrow>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{PO}}_4^{3-} $$</annotation>\n </semantics></math> = P (0.242 ± 0.049 mg/L) and <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>SiO</mi>\n <mn>3</mn>\n <mrow>\n <mn>2</mn>\n <mo>−</mo>\n </mrow>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{SiO}}_3^{2-} $$</annotation>\n </semantics></math> = Si (4.094 ± 0. 095 mg/L) were found in the water samples from station S-1, while the lowest values of <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NH</mi>\n <mn>4</mn>\n <mo>+</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NH}}_4^{+} $$</annotation>\n </semantics></math> (0.063 ± 0.007 mg/L), <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NO</mi>\n <mn>2</mn>\n <mo>−</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NO}}_2^{-} $$</annotation>\n </semantics></math> (0.0124 ± 0.001 mg/L), <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>NO</mi>\n <mn>3</mn>\n <mo>−</mo>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{NO}}_3^{-} $$</annotation>\n </semantics></math> (0.053 ± 0.003 mg/L), <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>PO</mi>\n <mn>4</mn>\n <mrow>\n <mn>3</mn>\n <mo>−</mo>\n </mrow>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{PO}}_4^{3-} $$</annotation>\n </semantics></math> = P (0.012 ± 0.002 mg/L) and <span></span><math>\n <semantics>\n <mrow>\n <msubsup>\n <mi>SiO</mi>\n <mn>3</mn>\n <mrow>\n <mn>2</mn>\n <mo>−</mo>\n </mrow>\n </msubsup>\n </mrow>\n <annotation>$$ {\\mathrm{SiO}}_3^{2-} $$</annotation>\n </semantics></math> (0.713 ± 0.009 mg/L) were recorded in station S-8. The order of nutrient values and bacterial count in the water and soil samples was same: S-1 > S-5 > S-3 > S-6 > S-4 > S-2 > S-7 > S-8. <i>Avicennia marina</i> was the only species found in all stations therefore; this species was considered for the assessment of the biomass of above- and belowground parts. The highest biomass (aboveground parts; 131.23 ± 2.09 Mg/ha, belowground parts; 139.86 ± 2.57 Mg/ha) was recorded at station S-1. The lowest biomass (aboveground parts; 119.72 ± 1.99 Mg/ha, belowground parts; 127.13 ± 2.01 Mg/ha) was found at station S-8. The analysis of organic matter (both water and soil samples) also showed the same trend. It was concluded that that mangrove biomass was nutrient-dependent, confirming our hypothesis that “mangrove biomass could depend on the availability of nutrients.” Mangrove ecosystem plays an important role in coastal and marine food webs and is closely connected to the well-being of coastal communities. Therefore, the mangrove ecosystem is mainly included in the United Nations Sustainable Development Goals (SDGs) and the Paris Agreement (climate change mitigation) in this decade. This study is in line with SDGs 12 (Responsible consumption and production of food), 13 (Climate action), 14 (Life below water) and 17 (Partnerships with the goals). The mangrove plants convert carbon dioxide (toxic form of carbon) in its useful form (biomass), and in addition, the mangrove ecosystem serves as a food and nursery area for fish and shellfish fisheries. Therefore, this research promotes the role of the mangrove ecosystem to benefit the blue economy and mitigate climate change. It was concluded that the abundance of bacteria and the biomass of mangroves depend on the availability of nutrients. Therefore, the results of this study strengthen our hypothesis. In the future, this study could serve as a reference study for blue carbon sequestration in the mangrove ecosystem.</p>","PeriodicalId":11467,"journal":{"name":"Ecology and Evolution","volume":"15 7","pages":""},"PeriodicalIF":2.3000,"publicationDate":"2025-07-04","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1002/ece3.71697","citationCount":"0","resultStr":"{\"title\":\"Determination of Nutrients, Biomass, and Bacterial Quantification in Different Mangroves Sites: A Comparative Study on Nutrients Dependent Biomass Production\",\"authors\":\"Sadar Aslam, You-Shao Wang\",\"doi\":\"10.1002/ece3.71697\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p>This study was conducted at eight different sites of the mangrove ecosystem in Kaozhou Yang, Huidong District, Huizhou Guangdong, South China Sea. The concentration of nutrients (<span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NH</mi>\\n <mn>4</mn>\\n <mo>+</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NH}}_4^{+} $$</annotation>\\n </semantics></math>, <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NO</mi>\\n <mn>2</mn>\\n <mo>−</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NO}}_2^{-} $$</annotation>\\n </semantics></math>, <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NO</mi>\\n <mn>3</mn>\\n <mo>−</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NO}}_3^{-} $$</annotation>\\n </semantics></math>, <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>PO</mi>\\n <mn>4</mn>\\n <mrow>\\n <mn>3</mn>\\n <mo>−</mo>\\n </mrow>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{PO}}_4^{3-} $$</annotation>\\n </semantics></math> and <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>SiO</mi>\\n <mn>3</mn>\\n <mrow>\\n <mn>2</mn>\\n <mo>−</mo>\\n </mrow>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{SiO}}_3^{2-} $$</annotation>\\n </semantics></math>) was determined (both water and soil samples). Based on the nutrient concentration, the comparison of mangrove biomass production, total organic matter and bacterial count were also investigated. The level of nutrient values and biomass production of mangrove and bacterial count in both water and soil samples followed the same trend. The results showed that the highest concentration of <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NH</mi>\\n <mn>4</mn>\\n <mo>+</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NH}}_4^{+} $$</annotation>\\n </semantics></math> (0.457 ± 0.051 mg/L), <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NO</mi>\\n <mn>2</mn>\\n <mo>−</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NO}}_2^{-} $$</annotation>\\n </semantics></math> (0.223 ± 0.018 mg/L), <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NO</mi>\\n <mn>3</mn>\\n <mo>−</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NO}}_3^{-} $$</annotation>\\n </semantics></math> (0.521 ± 0.038 mg/L), <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>PO</mi>\\n <mn>4</mn>\\n <mrow>\\n <mn>3</mn>\\n <mo>−</mo>\\n </mrow>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{PO}}_4^{3-} $$</annotation>\\n </semantics></math> = P (0.242 ± 0.049 mg/L) and <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>SiO</mi>\\n <mn>3</mn>\\n <mrow>\\n <mn>2</mn>\\n <mo>−</mo>\\n </mrow>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{SiO}}_3^{2-} $$</annotation>\\n </semantics></math> = Si (4.094 ± 0. 095 mg/L) were found in the water samples from station S-1, while the lowest values of <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NH</mi>\\n <mn>4</mn>\\n <mo>+</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NH}}_4^{+} $$</annotation>\\n </semantics></math> (0.063 ± 0.007 mg/L), <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NO</mi>\\n <mn>2</mn>\\n <mo>−</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NO}}_2^{-} $$</annotation>\\n </semantics></math> (0.0124 ± 0.001 mg/L), <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>NO</mi>\\n <mn>3</mn>\\n <mo>−</mo>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{NO}}_3^{-} $$</annotation>\\n </semantics></math> (0.053 ± 0.003 mg/L), <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>PO</mi>\\n <mn>4</mn>\\n <mrow>\\n <mn>3</mn>\\n <mo>−</mo>\\n </mrow>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{PO}}_4^{3-} $$</annotation>\\n </semantics></math> = P (0.012 ± 0.002 mg/L) and <span></span><math>\\n <semantics>\\n <mrow>\\n <msubsup>\\n <mi>SiO</mi>\\n <mn>3</mn>\\n <mrow>\\n <mn>2</mn>\\n <mo>−</mo>\\n </mrow>\\n </msubsup>\\n </mrow>\\n <annotation>$$ {\\\\mathrm{SiO}}_3^{2-} $$</annotation>\\n </semantics></math> (0.713 ± 0.009 mg/L) were recorded in station S-8. The order of nutrient values and bacterial count in the water and soil samples was same: S-1 > S-5 > S-3 > S-6 > S-4 > S-2 > S-7 > S-8. <i>Avicennia marina</i> was the only species found in all stations therefore; this species was considered for the assessment of the biomass of above- and belowground parts. The highest biomass (aboveground parts; 131.23 ± 2.09 Mg/ha, belowground parts; 139.86 ± 2.57 Mg/ha) was recorded at station S-1. The lowest biomass (aboveground parts; 119.72 ± 1.99 Mg/ha, belowground parts; 127.13 ± 2.01 Mg/ha) was found at station S-8. The analysis of organic matter (both water and soil samples) also showed the same trend. It was concluded that that mangrove biomass was nutrient-dependent, confirming our hypothesis that “mangrove biomass could depend on the availability of nutrients.” Mangrove ecosystem plays an important role in coastal and marine food webs and is closely connected to the well-being of coastal communities. Therefore, the mangrove ecosystem is mainly included in the United Nations Sustainable Development Goals (SDGs) and the Paris Agreement (climate change mitigation) in this decade. This study is in line with SDGs 12 (Responsible consumption and production of food), 13 (Climate action), 14 (Life below water) and 17 (Partnerships with the goals). The mangrove plants convert carbon dioxide (toxic form of carbon) in its useful form (biomass), and in addition, the mangrove ecosystem serves as a food and nursery area for fish and shellfish fisheries. Therefore, this research promotes the role of the mangrove ecosystem to benefit the blue economy and mitigate climate change. It was concluded that the abundance of bacteria and the biomass of mangroves depend on the availability of nutrients. Therefore, the results of this study strengthen our hypothesis. In the future, this study could serve as a reference study for blue carbon sequestration in the mangrove ecosystem.</p>\",\"PeriodicalId\":11467,\"journal\":{\"name\":\"Ecology and Evolution\",\"volume\":\"15 7\",\"pages\":\"\"},\"PeriodicalIF\":2.3000,\"publicationDate\":\"2025-07-04\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"https://onlinelibrary.wiley.com/doi/epdf/10.1002/ece3.71697\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Ecology and Evolution\",\"FirstCategoryId\":\"99\",\"ListUrlMain\":\"https://onlinelibrary.wiley.com/doi/10.1002/ece3.71697\",\"RegionNum\":2,\"RegionCategory\":\"生物学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q2\",\"JCRName\":\"ECOLOGY\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Ecology and Evolution","FirstCategoryId":"99","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1002/ece3.71697","RegionNum":2,"RegionCategory":"生物学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q2","JCRName":"ECOLOGY","Score":null,"Total":0}
Determination of Nutrients, Biomass, and Bacterial Quantification in Different Mangroves Sites: A Comparative Study on Nutrients Dependent Biomass Production
This study was conducted at eight different sites of the mangrove ecosystem in Kaozhou Yang, Huidong District, Huizhou Guangdong, South China Sea. The concentration of nutrients (, , , and ) was determined (both water and soil samples). Based on the nutrient concentration, the comparison of mangrove biomass production, total organic matter and bacterial count were also investigated. The level of nutrient values and biomass production of mangrove and bacterial count in both water and soil samples followed the same trend. The results showed that the highest concentration of (0.457 ± 0.051 mg/L), (0.223 ± 0.018 mg/L), (0.521 ± 0.038 mg/L), = P (0.242 ± 0.049 mg/L) and = Si (4.094 ± 0. 095 mg/L) were found in the water samples from station S-1, while the lowest values of (0.063 ± 0.007 mg/L), (0.0124 ± 0.001 mg/L), (0.053 ± 0.003 mg/L), = P (0.012 ± 0.002 mg/L) and (0.713 ± 0.009 mg/L) were recorded in station S-8. The order of nutrient values and bacterial count in the water and soil samples was same: S-1 > S-5 > S-3 > S-6 > S-4 > S-2 > S-7 > S-8. Avicennia marina was the only species found in all stations therefore; this species was considered for the assessment of the biomass of above- and belowground parts. The highest biomass (aboveground parts; 131.23 ± 2.09 Mg/ha, belowground parts; 139.86 ± 2.57 Mg/ha) was recorded at station S-1. The lowest biomass (aboveground parts; 119.72 ± 1.99 Mg/ha, belowground parts; 127.13 ± 2.01 Mg/ha) was found at station S-8. The analysis of organic matter (both water and soil samples) also showed the same trend. It was concluded that that mangrove biomass was nutrient-dependent, confirming our hypothesis that “mangrove biomass could depend on the availability of nutrients.” Mangrove ecosystem plays an important role in coastal and marine food webs and is closely connected to the well-being of coastal communities. Therefore, the mangrove ecosystem is mainly included in the United Nations Sustainable Development Goals (SDGs) and the Paris Agreement (climate change mitigation) in this decade. This study is in line with SDGs 12 (Responsible consumption and production of food), 13 (Climate action), 14 (Life below water) and 17 (Partnerships with the goals). The mangrove plants convert carbon dioxide (toxic form of carbon) in its useful form (biomass), and in addition, the mangrove ecosystem serves as a food and nursery area for fish and shellfish fisheries. Therefore, this research promotes the role of the mangrove ecosystem to benefit the blue economy and mitigate climate change. It was concluded that the abundance of bacteria and the biomass of mangroves depend on the availability of nutrients. Therefore, the results of this study strengthen our hypothesis. In the future, this study could serve as a reference study for blue carbon sequestration in the mangrove ecosystem.
期刊介绍:
Ecology and Evolution is the peer reviewed journal for rapid dissemination of research in all areas of ecology, evolution and conservation science. The journal gives priority to quality research reports, theoretical or empirical, that develop our understanding of organisms and their diversity, interactions between them, and the natural environment.
Ecology and Evolution gives prompt and equal consideration to papers reporting theoretical, experimental, applied and descriptive work in terrestrial and aquatic environments. The journal will consider submissions across taxa in areas including but not limited to micro and macro ecological and evolutionary processes, characteristics of and interactions between individuals, populations, communities and the environment, physiological responses to environmental change, population genetics and phylogenetics, relatedness and kin selection, life histories, systematics and taxonomy, conservation genetics, extinction, speciation, adaption, behaviour, biodiversity, species abundance, macroecology, population and ecosystem dynamics, and conservation policy.