Special Commentary on Maximum Acceptable Toxicant Concentration (MATC)

2019 ◽  
Vol 4 (2) ◽  
pp. 37-38
Author(s):  
K.S. Rao
Keyword(s):  
Toxicant Concentration

Effects of Long-Term Exposure to Carbaryl (Sevin) on Survival, Growth, and Reproduction of the Fathead Minnow (Pimephales promelas)

1972 ◽  
Vol 29 (5) ◽  
pp. 583-587 ◽  
Author(s):  
A. R. Carlson
Keyword(s):  
Life Cycle ◽  
Fathead Minnow ◽  
Pimephales Promelas ◽  
Threshold Concentration ◽  
Fathead Minnows ◽  
Motile Sperm ◽  
High Concentration ◽  
Toxicant Concentration ◽  
Growth And Reproduction

When fathead minnows (Pimephales promelas) were exposed to five concentrations (0.008–0.68 mg/liter) of the insecticide carbaryl for 9 months and throughout a life cycle, the highest concentration prevented reproduction and decreased survival. At the high concentration, testes contained motile sperm and ovaries were in a flaccid condition and appeared to be in a resorptive state. At the 0.68 mg/liter concentration, carbaryl appeared to contribute to mortality of larvae (produced by unexposed parents) within 30 days of hatching. Survival of young grown in the 0.008 mg/liter concentration was reduced. Since no demonstrable effects were noted for survival, growth, or reproduction at the 0.017, 0.062, and 0.21 mg/liter concentrations, this low survival value is considered not due to carbaryl. The 96-hr median tolerance concentration (TL 50) and the lethal threshold concentration (LTC) for 2-month-old fathead minnows were 9.0 mg/liter. The maximum acceptable toxicant concentration (MATC) for fathead minnows exposed to carbaryl in water with a hardness of 45.2 mg/liter and a pH of 7.5 lies between 0.21 and 0.68 mg/liter. The application factors (MATC/96-hr TL50 and MATC/LTC) both lie between 0.023 and 0.075.

scholarly journals Early determination of toxicant concentration in water supply using MHE

2010 ◽  
Vol 44 (10) ◽  
pp. 3252-3260 ◽  
Author(s):  
F. Ibrahim ◽  
B. Huang ◽  
J. Xing ◽  
S. Gabos
Keyword(s):  
Water Supply ◽  
Toxicant Concentration

scholarly journals Captan Toxicity to Fathead Minnows (Pimephales promelas), Bluegills (Lepomis macrochirus), and Brook Trout (Salvelinus fontinalis)

1973 ◽  
Vol 30 (12) ◽  
pp. 1811-1817 ◽  
Author(s):  
Roger O. Hermanutz ◽  
Leonard H. Mueller ◽  
Kenneth D. Kempfert
Keyword(s):  
Brook Trout ◽  
Salvelinus Fontinalis ◽  
Pimephales Promelas ◽  
Lepomis Macrochirus ◽  
Threshold Concentration ◽  
Fathead Minnows ◽  
Toxicant Concentration ◽  
Flow Through ◽  
Survival And Growth ◽  
Growth And Reproduction

The toxic effects of captan on survival, growth, and reproduction of fathead minnows (Pimephales promelas) and on survival of bluegills (Lepomis macrochirus) and brook trout (Salvelinus fontinalis) were determined in a flow-through system. In a 45-week exposure of fathead minnows, survival and growth were adversely affected at 39.5 μg/liter. Adverse effects on spawning were suspected but not statistically demonstrated at 39.5 and 16.5 μg/liter. The maximum acceptable toxicant concentration (MATC), based on survival and growth, lies between 39.5 and 16.5 μg/liter. The lethal threshold concentration (LTC) derived from acute exposures was 64 μg/liter, resulting in an application factor (MATC/LTC) between 0.26 and 0.62. LTC values for the bluegill and brook trout were 72 and 29 μg/liter, respectively. The estimated MATC is between 44.6 and 18.7 μg/liter for the bluegill and between 18.0 and 7.5 μg/liter for the brook trout.The half-life of captan in Lake Superior water with a pH of 7.6 is about 7 hr at 12 C and about 1 hr at 25 C. Breakdown products from an initial 550 μg/liter of captan were not lethal to 3-month-old fathead minnows.

scholarly journals The Effect of Profenofos on the Nutritive Composition of Major Carp for Estimating Maximum Allowable Toxicant Concentration of the Pesticide

2019 ◽  
Vol 28 (3) ◽  
pp. 1127-1133
Author(s):  
Ghazala Ghazla ◽  
Salma Sultana ◽  
K. Al-Ghanim ◽  
Shahid Mahboob
Keyword(s):  
Toxicant Concentration ◽  
Nutritive Composition

scholarly journals The Toxic Effects of Lindane On Microcystis Aeruginosa And The Influence of pH And DOM Dependent Effects of Lindane On Microcystis Aeruginosa

2021 ◽  
Author(s):  
Deng Xiru ◽  
Jiang Yingnan ◽  
Xian Qiming
Keyword(s):  
Microcystis Aeruginosa ◽  
Total Protein ◽  
Culture Conditions ◽  
Toxic Effects ◽  
Maximal Effect ◽  
Sod Activity ◽  
Protein Levels ◽  
Toxicant Concentration ◽  
Effect Concentration ◽  
Influence Of Ph

Abstract The toxic effects of Lindane (γ-BHC) on Microcystis aeruginosa were studied under lab culture conditions. Total protein levels, as well as malondialdehyde (MDA) levels and superoxide dismutase (SOD) enzyme activity, in algal cells, were determined after exposure to different concentrations of Lindane. The bioaccumulation of Lindane, as well as the influence of pH and dissolved organic matter (DOM), on the toxic effects was also evaluated in algal cells. The growth of M. aeruginosa was inhibited by Lindane treatment (96 h), resulting in 50% of maximal effect (EC50) concentration of 442 μg/L. In addition the lowest observed effect concentration (LOEC) was found to be 120 μg/L, the no observed effect concentration (NOEC) 60 μg/L, and the maximum acceptable toxicant concentration (MATC) 85 μg/L. With increasing concentrations of Lindane and exposure time, M. aeruginosa growth was significantly inhibited; in addition, total protein levels and SOD activity significantly decreased. MDA concentration, however, showed an insignificant increase after 96 h. Lindane has the potential for bioaccumulation in algal cells with a bioconcentration factor (BCF) of 340. Furthermore, the toxic effects of Lindane on M. aeruginosa were influenced by environmental factors, such as pH and DOM. The toxic effects decreased with increasing pH and humic acid concentrations. Ultrastructure cell images were used to depict Lindane induced apoptosis.

scholarly journals Can Early Life-Stages of the Marine FishSparus auratabe Useful for the Evaluation of the Toxicity of Linear Alkylbenzene Sulphonates Homologues (LAS C10-C14) and Commercial LAS?

2002 ◽  
Vol 2 ◽  
pp. 1689-1698 ◽  
Author(s):  
M. Hampel ◽  
I. Moreno-Garrido ◽  
J. Blasco
Keyword(s):  
Early Life ◽  
Sparus Aurata ◽  
Life Stage ◽  
Early Life Stage ◽  
Toxicity Tests ◽  
Linear Alkylbenzene ◽  
Cleaning Agents ◽  
Pollutant Concentrations ◽  
Toxicant Concentration ◽  
Receiving Waters

Most commercial household cleaning agents and personal care products contain the anionic surfactant linear alkylbenzene sulphonates (LAS) as the active compound. After their use they are discharged, theoretically after adequate wastewater treatment, into receiving waters finally reaching estuaries and coastal waters. Laboratory toxicity tests are useful tools in determining at which concentration a certain wastewater compound becomes hazardous for an existing group of organisms. Early life-stage toxicity tests include exposure during the most sensitive development period of the organism. In fish, this type of assay has shown to predict accurately maximum acceptable toxicant concentration (MATC) values (comprised in the range defined by the NOEC and LOEC) in fish early life-stage tests. For this reason, larvae of the seabream, Sparus aurata, were exposed to increasing concentrations of LAS homologues (C10-C14) and commercial LAS. Obtained LC50values ranged between 0.1 and 3.0 mg l-1and were compared with LC50values of previous hatching experiments with the same species. Larvae proved to be more sensitive to LAS exposure of individual homologues than eggs, except in the case of commercial LAS. LC50values can be directly employed to determine their potential risk in a concrete environment with known pollutant concentrations. Dividing the LC50value with the found homologue concentration and extrapolating with certain security factors proposed by different environmental organisms, potentially hazardous pollutant concentrations may be detected. Average estuarine or coastal LAS concentrations are generally below toxicity limits for this kind of organism, considering that the average alkyl chain length of commercial LAS is 11.6 carbon atoms.

Long-Term Effects of Lead Exposure on Three Generations of Brook Trout (Salvelinus fontinalis)

1976 ◽  
Vol 33 (8) ◽  
pp. 1731-1741 ◽  
Author(s):  
G. W. Holcombe ◽  
D. A. Benoit ◽  
E. N. Leonard ◽  
J. M. McKim
Keyword(s):  
Brook Trout ◽  
Second Generation ◽  
Salvelinus Fontinalis ◽  
Residue Analysis ◽  
Kidney Tissue ◽  
Third Generation ◽  
Long Term Effects ◽  
Three Generations ◽  
Toxicant Concentration ◽  
Liver And Kidney

Exposure of three generations of brook trout (Salvelinus fontinalis) to mean total lead concentrations (0.9–474 μg/liter) showed that all second-generation trout exposed to 235 and 474 μg Pb/liter and 34% of those exposed to 119 μg Pb/liter developed severe spinal deformities (scoliosis). Scoliosis also appeared in 21% of the newly hatched third-generation alevins exposed to 119 μg Pb/liter, and weights of these fish 12 wk after hatch were significantly reduced. Gill, liver, and kidney tissues of first- and second-generation brook trout accumulated the greatest amount of lead. Only small amounts accumulated in the edible muscle. An equilibrium of lead residues was reached in liver and kidney tissue from second-generation fish after 70 wk of exposure, but not in gill tissue. Fish exposed to 119 μg Pb/liter and then placed in uncontaminated control water for 12 wk showed a 70, 78, and 74% loss in micrograms Pb per gram for gill, liver, and kidney tissue, respectively, and a 39, 56, and 35% loss, respectively, in the total micrograms of Pb in the whole tissue. Residue analysis of eggs, alevins, and juveniles showed that lead was accumulated during these life stages. The maximum acceptable toxicant concentration (MATC) for brook trout in water with a hardness of 44 mg/liter (as CaCO3) and a pH of 6.8–7.6 lies between 58 and 119 μg/liter for total lead and between 39 and 84 μg/liter for dissolved lead. The MATC was based on the development of scoliosis in second- and third-generation fish and the reduced growth of 12-wk-old third-generation trout. The 96-h LC50 for brook trout was 4100 μg/liter based on total lead and 3362 μg/liter based on dissolved lead; therefore, the application factor (MATC/96-h LC50) lies between 0.012 and 0.029 for both total and dissolved lead.

Deposit structure and efficacy of pesticide application. 1: Interactions between deposit size, toxicant concentration and deposit number

1999 ◽  
Vol 55 (8) ◽  
pp. 783-792 ◽  
Author(s):  
Timothy A Ebert ◽  
Robin A J Taylor ◽  
Roger A Downer ◽  
Franklin R Hall
Keyword(s):  
Pesticide Application ◽  
Toxicant Concentration ◽  
Deposit Structure
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