Risk Assessment Based on Nitrogen and Phosphorus Forms in Watershed Sediments: A Case Study of the Upper Reaches of the Minjiang Watershed

Abstract

In order to achieve effective eutrophication control and ecosystem restoration, it is of great significance to investigate the distribution characteristics of nutrient elements in sediments, and to perform ecological risk assessments. In the current grading criteria for nutrient elements in sediments, only the overall or organic components of carbon, nitrogen and phosphorus are considered, while the specific species distributions and bioavailability characteristics are rarely taken into account. Hence, using the current grading criteria, the differences in the release, migration and biological activity of nutrient elements in sediments cannot be accurately reflected. Taking the upper reaches of the Minjiang River watershed as an example, we analyzed the overall distributions and the ratio of nutrient elements in sediments, the spatial changes of nitrogen and phosphorus forms, the bioavailability, and the environmental significance. The ecological risk of nitrogen and phosphorus in sediments was assessed using an evaluation method based upon the biological effective parameter. The results were compared with the results of the evaluation methods based on the single pollution index, and then these evaluation methods were confirmed accordingly. From the results, the following conclusions can be obtained: (1) The spatial distributions of nutrient elements in sediments in the upper reaches of the Minjiang River Watershed (including the Jianxi Basin, Futunxi Basin, and Shaxi Basin) were significantly affected by the local ecology and the urban sewage discharge system. (2) The maximum average contents of total organic carbon (TOC), total nitrogen (TN), and total phosphorus (TP) in sediments were observed in the Jianxi Basin, the Futunxi Basin and the Shaxi Basin, respectively. (3) According to the contents of nitrogen and phosphorus in sediments, the bioavailable nitrogen (TTN) accounted for 35.49% of the total contents of TN. The components of TTN can be sorted from high to low as follows: Nitrogen in organic sulfide form (SOEF-N) > nitrogen in iron-manganese oxide form (SAEF-N) > nitrogen in ion exchange form (IEF-N) > nitrogen in weak acid leaching form (WAEF-N). Inorganic phosphorus (IP) was the main component of TP. The components of IP can be sorted from high to low as follows: Metal oxide bound phosphorus (NaOH-P) > calcium bound phosphorus (HCl-P) > reduced phosphorus (BD-P) > weakly adsorbed phosphorus (NH4Cl-P). Meanwhile, bioavailable phosphorus (BAP, BAP = NH4Cl-P + BD-P + NaOH-P) accounted for 36.94% of TP. According to the results of the single pollution index method, the risk level of TOC pollution in the sediments was relatively low in the whole area, while the risk level of TN pollution was low or moderate in most zones, and severe in certain ones. The risk level of TP pollution was low to moderate. (4) From the results of the bioavailability index evaluation method, based on the total amounts and forms of N and P, the risk level of N pollution was moderate, while the risk of P pollution was negligible. In addition, the results of the bioavailability index evaluation method were more consistent with the actual situation and reflected the overall environmental effects of nitrogen and phosphorus.

The Effects of Land Use on Concentrations of Nutrients and Selected Metals in Bottom Sediments and the Risk Assessment for Rivers of the Warta River Catchment, Poland

“…An ecological risk assessment of nutrients in river bottom sediments was performed using a method based on the Single Pollution Index (SPI) [43].…”

“…Values of 550 mg-kg −1 , 600 mg-kg −1 , 1% and 2% were used as standard values for TN, TP, TOC and Fe, respectively, which are derived from safe nutrient concentration limits that can be found in the Sediment Quality Guidelines [25,43]. Based on the P i , four hazard classes can be distinguished as shown in Table 2 [43].…”

“…Values of 550 mg-kg −1 , 600 mg-kg −1 , 1% and 2% were used as standard values for TN, TP, TOC and Fe, respectively, which are derived from safe nutrient concentration limits that can be found in the Sediment Quality Guidelines [25,43]. Based on the P i , four hazard classes can be distinguished as shown in Table 2 [43]. C:P:N stoichiometry enables the description of potential sources of pollution as well as geochemical and biochemical processes occurring in the environment [31,44].…”

“…C:P:N stoichiometry enables the description of potential sources of pollution as well as geochemical and biochemical processes occurring in the environment [31,44]. TOC/TN is one of more frequently used ratios, which identifies potential sources of organic matter [43]. TOC/TP reflects to some extent the rate of conversion of organic carbon and phosphorus compounds [45].…”

Targeting Remediation Dredging by Ecological Risk Assessment of Heavy Metals in Lake Sediment: A Case Study of Shitang Lake, China

“…Additionally, these lakes play a vital role in population and industrial centers [1]. However, increasing industrial wastewater and domestic sewage are deteriorating water quality, degrading the ecosystem, and causing eutrophication and other problems [2][3][4]. The anthropogenic impact on the lake waters include a significant heavy metal load which easily accumulates in lake sediment and are sources of sustained pollution.…”