Algal blooms and cyanotoxins in Jordan Lake, North Carolina

40Citations
Citations of this article
106Readers
Mendeley users who have this article in their library.

Abstract

The eutrophication of waterways has led to a rise in cyanobacterial, harmful algal blooms (CyanoHABs) worldwide. The deterioration of water quality due to excess algal biomass in lakes has been well documented (e.g., water clarity, hypoxic conditions), but health risks associated with cyanotoxins remain largely unexplored in the absence of toxin information. This study is the first to document the presence of dissolved microcystin, anatoxin-a, cylindrospermopsin, and β-N-methylamino-L-alanine in Jordan Lake, a major drinking water reservoir in North Carolina. Saxitoxin presence was not confirmed. Multiple toxins were detected at 86% of the tested sites and during 44% of the sampling events between 2014 and 2016. Although concentrations were low, continued exposure of organisms to multiple toxins raises some concerns. A combination of discrete sampling and in-situ tracking (Solid Phase Adsorption Toxin Tracking [SPATT]) revealed that microcystin and anatoxin were the most pervasive year-round. Between 2011 and 2016, summer and fall blooms were dominated by the same cyanobacterial genera, all of which are suggested producers of single or multiple cyanotoxins. The study’s findings provide further evidence of the ubiquitous nature of cyanotoxins, and the challenges involved in linking CyanoHAB dynamics to specific environmental forcing factors are discussed.

Figures

  • Figure 1. Map of Jordan Lake sampling sites. Biological, chemical and physical data were analyzed over a 6-year period (2011 to 2016) for sites A, B and C (red circles). Information over approximately 2 years (2014 to 2016) was available for an additional six sites (sites D through I, blue circles). Arrows indicate the three main rivers flowing into the lake. Map from snazzymaps.com.
  • Table 1. Latitude (Lat) and longitude (Long) for the nine sampling sites across Jordan Lake. Sampling was conducted on a monthly basis with more frequent biweekly monitoring during months with higher bloom activity (May through September). Included are the Site ID and Division of Water Resources (DWR) site names. n = number of sampling time points per site. Depth describes the average water column depth.
  • Figure 3. Cyanobacterial cell densities at each of the sampling locations (sites A through I are shown as panels A through I). Colors depict the six most abundant genera, and less abundant taxa are grouped as “Other”. Long-term sites A through C were sampled from January 2011 to December 2016. D, F, H and I were monitored from October 2014 to June 2016, while monitoring at E and G continued through December 2016. Vertical dashed lines separate years. Note, there are differing scales on the y-axes for A, C and E.
  • Figure 4. (A) MDS plot based on Bray–Curtis similarities for cyanobacterial communities as a nonmetric multi-dimensional scaling (nMDS) plot by season (data from all years and stations combined). (B) Relative changes in cyanobacterial community composition shown along a month-to-month trajectory (site A in 2015). Stress values are reported in the top right corner of each plot.
  • Figure 5. Changes in (A) temperature, (B) NOx, (C) NH3 concentration and (D) Total Kjeldahl nitrogen (TKN):TP ratio averaged for each sampling event. Standard error bars are included. Vertical dashed lines separate years.
  • Figure 6. MDS plot showing Euclidian distances for environmental fingerprints by season. Parameters included in these analyses were temperature, NOx, NH3, TKN, TP and DO concentrations, TKN:TP ratios, pH levels and turbidity. The stress value is reported in the top right corner.
  • Figure 6. MDS plot showing Euclidian distances for environmental fingerprints by season. Parameters included in these analyses were temperature, NOx, NH3, TKN, TP and DO concentrations, TKN:TP ratios, pH levels and turbidity. The stress value is reported in the top right corner.
  • Table 2. Percentage (%) of samples that tested positive for varying toxins using discrete sampling and the Solid Phase Adsorption Toxin Tracking (SPATTs) approach. Average concentrations (Ave) for dissolved (Diss) toxins are shown as µg L−1 (values below LDL were not included when calculating the average for each toxin), and for SPATT as ng toxin (g resin)1 d−1. n = number of samples tested. LDL = low detection limit of Enzyme-Linked Immunosorbent Assay (ELISA) detection method; BDL = below detection limit of ELISA test; MCY = microcystin; ANA = anatoxin-a; CYN = cylindrospermopsin; BMAA = β-N-methylamino-L-alanine; STX = saxitoxin.

Register to see more suggestions

Mendeley helps you to discover research relevant for your work.

Already have an account?

Cite

CITATION STYLE

APA

Wiltsie, D., Schnetzer, A., Green, J., Borgh, M. V., & Fensin, E. (2018). Algal blooms and cyanotoxins in Jordan Lake, North Carolina. Toxins, 10(2). https://doi.org/10.3390/toxins10020092

Readers over time

‘18‘19‘20‘21‘22‘23‘24‘2509182736

Readers' Seniority

Tooltip

PhD / Post grad / Masters / Doc 42

58%

Researcher 22

30%

Professor / Associate Prof. 6

8%

Lecturer / Post doc 3

4%

Readers' Discipline

Tooltip

Environmental Science 19

35%

Engineering 14

26%

Agricultural and Biological Sciences 12

22%

Chemistry 9

17%

Article Metrics

Tooltip
Mentions
Blog Mentions: 1
News Mentions: 10
Social Media
Shares, Likes & Comments: 13

Save time finding and organizing research with Mendeley

Sign up for free
0