Modeling of the Atmospheric Process of Cyanobacterial Toxins in Algal Aerosol

被引:1
|
作者
Zorbas, Victoria [1 ]
Jang, Myoseon [1 ]
Emam, Baharan [1 ,2 ]
Choi, Jiwon [1 ]
机构
[1] Univ Florida, Dept Environm Engn Sci, Gainesville, FL 32611 USA
[2] Shahid Beheshti Univ Med Sci, Sch Publ Hlth & Safety, Dept Environm Hlth Engn, Tehran 1983535511, Iran
来源
ACS EARTH AND SPACE CHEMISTRY | 2023年 / 7卷 / 05期
基金
美国国家科学基金会;
关键词
harmful algal blooms; microcystin-LR; cyanobacterial algae; atmospheric oxidation; algal aerosol; MICROCYSTIN-LR; WATER; PHOTOOXIDATION; BLOOMS; HYDROCARBONS; CHEMISTRY; RR;
D O I
10.1021/acsearthspacechem.3c00050
中图分类号
O6 [化学];
学科分类号
0703 ;
摘要
The degradation of microcystin-LR (MC-LR) in cyanobacterial aerosol with atmospheric oxidants, such as ozone and OH radicals, was predicted by the Harmful Algal Aerosol Reaction (HAAR) model. The ozonolysis of MC-LR in cyanobacterial aerosol at nighttime and its photooxidation during the daytime was observed in an outdoor chamber. The HAAR model simulates the impact of humidity and aerosol compositions on MC-LR decay. In the model, gas-particle partitioning of atmospheric oxidants onto algal aerosol was kinetically treated using the absorption and desorption processes. In the model simulation, the half-life of MC-LR estimated with its ozonolysis rate constant (3 x 10-11cc/molecules/s) is 4.6 h +/- 0.92 at 66 ppb ozone. With the reaction rate constant for MC-LR with OH radicals (6 x 10-7 cc/molecules/s), the estimated half-life of MC-LR during daytime under Florida's typical summer sunlight is 6 minutes, suggesting that the reaction with OH radicals dominates daytime MC-LR decay. Under moderate sunlight with a typical wind speed (9.2 km/h), the dispersion and HAAR models predict that 25% of aerosolized MC-LR undergoes the atmospheric process within 0.92 km from a bloom source in Florida's largest lake, suggesting the critical role of the atmospheric oxidation of MCLR decay.
引用
收藏
页码:1141 / 1150
页数:10
相关论文
共 50 条
  • [41] Health aspects of freshwater cyanobacterial toxins
    Shaw, G.
    Lam, P. K. S.
    Sustainable and Safe Water Supplies, 2007, 7 (02): : 193 - 203
  • [42] The occurrence of cyanobacterial toxins in Lake Champlain
    Boyer, GL
    Watzin, MC
    Shambaugh, AD
    Satchwell, MF
    Rosen, BH
    Mihuc, T
    LAKE CHAMPLAIN: PARTNERSHIPS AND RESEARCH IN THE NEW MILLENNIUM, 2004, : 241 - 257
  • [43] TESTING FOR ALGAL TOXINS INVITRO
    AUNE, T
    ATLA-ALTERNATIVES TO LABORATORY ANIMALS, 1987, 14 (03): : 172 - 173
  • [44] Destruction of cyanobacterial toxins by semiconductor photocatalysis
    Robertson, PKJ
    Lawton, LA
    Munch, B
    Rouzade, J
    CHEMICAL COMMUNICATIONS, 1997, (04) : 393 - 394
  • [45] Cyanobacterial toxins: Effects and control measures
    Rao, PVL
    PHARMACOLOGICAL PERSPECTIVES OF TOXIC CHEMICALS AND THEIR ANTIDOTES, 2004, : 179 - 196
  • [46] A rapid microbiotest for the detection of cyanobacterial toxins
    Torokne, Andrea
    Vasdinnyei, Rita
    Asztalos, B. Maria
    ENVIRONMENTAL TOXICOLOGY, 2007, 22 (01) : 64 - 68
  • [47] Water Blooms and Cyanobacterial Toxins in Lakes
    Jakubowska, Natalia
    Zagajewski, Pawel
    Goldyn, Ryszard
    POLISH JOURNAL OF ENVIRONMENTAL STUDIES, 2013, 22 (04): : 1077 - 1082
  • [48] PRODUCTION, DETECTION, AND QUANTIFICATION OF CYANOBACTERIAL TOXINS
    CODD, GA
    BROOKS, WP
    PRIESTLEY, IM
    POON, GK
    BELL, SG
    FAWELL, JK
    TOXICITY ASSESSMENT, 1989, 4 (04): : 499 - 511
  • [49] Cyanobacterial toxins: a growing environmental concern
    Haider, S
    Naithani, V
    Viswanathan, PN
    Kakkar, P
    CHEMOSPHERE, 2003, 52 (01) : 1 - 21
  • [50] Cyanobacterial toxins in Lake Baringo, Kenya
    Ballot, A
    Pflugmacher, S
    Wiegand, C
    Kotut, K
    Krienitz, L
    LIMNOLOGICA, 2003, 33 (01): : 2 - 9