Organic Chemistry: Current Research

Organic Chemistry: Current Research
Open Access

ISSN: 2161-0401

+44 1478 350008

Research Article - (2014) Volume 3, Issue 1

Theoretical Descriptor for the Correlation of the Fish Embryo Toxicity test (FET) By QSAR Model of LC50

Jining L, Deling F, Lei W, Linjun Z and Lili S*
Nanjing Institute of Environmental Sciences, Ministry of Environmental Protection, Nanjing, 210042, China
*Corresponding Author: Lili S, Nanjing Institute of Environmental Sciences, Ministry of Environmental Protection, Nanjing, 210042, China, Tel: +86 25 8528 7074, Fax: +86 25 8547 6477 Email:

Abstract

Quantitative structure–toxicity relationships were developed for the prediction of the fish embryo toxicity test using the CODESSA treatment, based on the linear heuristic method (HM) and support vector machines (SVM). Each kind of compound was represented by several calculated structural descriptors, derived for a diverse set of 97 compounds using DFT- B3LYP/6-31+G (d) level of the theory. A six-parameter correlation was found for the 97 compounds. In the HM method, the value of square of the correlation coefficient r2 is 0.8142, s2 is 0.0380, in the SVM method, the value of the r2 is 0.7105 and s2 is 0.0604. The HM model may be used for prediction of toxicity, safety and risk assessment of chemicals to achieve better ecotoxicological management.

Keywords: Fish Embryo Toxicity

Introduction

The fish acute toxicity is a mandatory component in the base set of data requirements for eco-toxicity testing but fish suffer distress and perhaps pain [1]. Animal alternative considerations have also been incorporated into new REACH regulations through strong advocacy for the reduction of testing with live animals. REACH, as a regulatory tool, was envisaged to revise the existing chemical policy and to harmonize chemical legislations in Europe and the major aim of REACH is to systematically evaluate the risk to human health and the environment of approximately 30,000 chemical substances [2]. The fish embryo toxicity (FET) testan alternative approach to classical acute fish toxicity testing with live fish, has been a mandatory component in routine whole effluent testing in Germany since 2005 and has already been standardized at the international level. A modified version has been submitted by the German Federal Environment Agency (UBA) as a draft guideline for an alternative to chemical testing with intact fish [1]. The fish embryo test is a surrogate for the OECD 203 acute fish toxicity test (or other guideline equivalent acute fish assays). Recently, the regulations of the People’s Republic of China on Control over Safety of Hazard Chemicals revised and passed, therefore, FET is useful for the acute fish toxicity testing. In order to analyze the applicability of the FET also in chemical testing, a comparative re-evaluation was carried out for a total of 97 substances, and QSAR was developed to evaluate fish embryo toxicity data. QSAR to evaluate fish embryo toxicity data is described to be useful for future validation exercises.

The quantitative structure-property/activity relationship (QSPR/ QSAR) method is based on the assumption that the variation of the behavior of the compounds, as expressed by many measured physicochemical properties, can be correlated with changes in molecular features of the compounds termed descriptors [3]. This method can be used for the prediction of the properties of new compounds. It can also be applied to identify and describe important structural features of the molecules that are relevant to variations in molecular properties. Computational models are useful because they rationalize a large number of experimental observations.

The QSAR model is widely used for the prediction of physicochemical properties and biological activities in chemical, environmental, and pharmaceutical areas [4,5], a potential or useful technique to estimate the toxicity especially for the compounds whose toxicity are not easy to test. The advantage of this approach over the experimental method lies in the fact that the descriptors used can be calculated from the structures alone and are not dependent on any experimental properties. Once the structure of a compound is known, a limited set of molecular properties, said descriptors, which can be obtained observing the molecular structure or semi-empirical quantum-mechanical calculations [6]. Therefore, once a reliable model is established, the model can be applied to help in identifying and describe important structural features of the molecules that are relevant to variations in molecular properties.

In this work we proposed a QSAR model to evaluate fish embryo toxicity data. 97 structures are calculated by the CODESSA software package, developed by Katritzky et al. [7,8] based on descriptors constitutional, topological, geometrical, geometrical, electrostatic and quantum chemical.

Materials And Methods

In order to develop the QSAR, a database of LC50, reported in terms of micromolar (μM) concentration for correlation purposes, reported LC50 values were converted to their molar units and subsequently to free energy related negative logarithmic state, i.e., log (1/ LC50). These LC50 values have been obtained from experiments and literature [9]. The selected series consists of total 97 numbers of compounds, divided in to two data sets, one was training set having 83 compounds and other was test set with the remaining 14 compounds based on random selection criteria. The biological activities were expressed in terms of median lethal concentration (EC50). their vibrational frequencies calculated at the DFT level relying on the B3LYP functional. A comparison of all the methods, namely, AM1, MP3, HF, and DFT/B3LYP, indicates that the DFT/B3LYP method is more reliable than others and has a high predictive power [12]. After optimization, the CODESSA program was used to calculate five types of molecular descriptors constitutional (number of various types of atoms and bonds, number of rings, molecular weight, etc.), topological (Wiener index, Randic indices, Kier -Hall shape indices, etc.), geometrical (moments of inertia, molecular volume, molecular surface area, etc.), electrostatic (minimum and maximum partial charges, polarity parameter, charged partial surface area descriptors, etc.), and quantum chemical (reactivity indices, dipole moment, HOMO and LUMO energies, etc.). In the framework of the CODESSA program, the statistical structure-property correlation techniques can be used for the analysis of user-submitted experimental data in combination with the calculated molecular descriptors.

Development of linear model by HM [13]

The heuristic procedure was used to obtain quantitative structure property relationship. Once the molecular descriptors are generated, the HM in CODESSA is used to pre-select the descriptors and build the near model. The advantages of the HM are the high speed, usually produces correlations 2–5 times faster than other methods with comparable quality and no software restrictions on the size of the data set [14]. The HM can either quickly give a good estimation about what quality of correlation to expect from the data, or derive several best regression models. HM of the descriptors selection proceeds with a pre-selection of the descriptors to eliminate: (1) those descriptors that are not available for each structure;(2) descriptors having a small variation in magnitude for all structures;(3)descriptors that provide a F-test value below 1.0 on the one-parameter correlation and (4) and the descriptors whose t-values are less than the user-specified value, etc. New descriptors were added one by one until the suitable number descriptors without losing any important information in the model is achieved [15]. The final result is a list of the 10 best models according to the values of the F-test and correlation coefficient. The statistical quality of the generated models was gauged by the F-test (F), squared correlation co-efficient (R2), square of cross-validate coefficient regression (RCV 2), t-test and the standard deviation (s2). Fischer’s value (F), which represents F-ratio between the variance of calculated and observed activity, and chance statistics assuring that the results are not merely based on chance correlations and t-test reflects significance of the parameter within the model. From the above processes, seven descriptors are selected from descriptors pool and the linear model is produced by the HM [16]. The experimental values of all compounds are summarized in Table 1.

NO. Compounds status MW Experimental
(μg//L)
HM
(μg//L)
SVM
(μg//L)
1 2-Aminoethanol Training 61.08 6.5662 4.5114 4.8806
2 4-Aminophenol Training 109.13 2.6720 1.8662 2.2334
3 Benzoicacid Training 122.12 4.3031 2.1385 2.3162
4 4-Bromoindole Training 195.95 3.6720 1.678 1.4798
5 5-Bromoindole Training 196.05 3.7250 1.7252 1.5358
6 6-Bromoindole Training 196.05 3.96426 2.3408 2.2578
7 2-Bromophenol Training 173.01 4.6543 2.0823 2.2993
8 3-Bromophenol Training 173.01 4.7829 3.2246 2.7912
9 4-Bromophenol Training 173.01 4.6657 3.3539 2.9999
10 n-Butylamine Training 73.14 4.5552 3.743 2.408
11 sec-Butylamine Training 73.14 4.9784 2.0591 2.2457
12 Butyldiglycol Training 162.23 6.1077 1.8154 2.3225
13 2-Chloroaniline Training 127.6 4.4517 3.8754 2.8491
14 3-Chloroaniline Training 127.6 4.3222 3.0148 2.7056
15 4-Chloroaniline Training 127.6 4.3280 1.7793 1.5822
16 4-Chlorophenol Training 128.56 4.5800 1.6495 2.0511
17 Cyclohexanol Training 100.16 6.1405 1.9123 2.32
18 Cyclohexylamine Training 99.18 4.8019 2.7298 2.5952
19 n-Decylamine Training 157.3 3.4977 1.4561 2.0633
20 2,4-Dibromophenol Training 251.9 3.9003 1.4761 2.0776
21 2,6-Dibromophenol Training 251.9 4.6208 3.8754 2.8491
22 Dibutylamine Training 129.25 4.6069 3.3737 2.9902
23 2,4-Dichloroaniline Training 162.02 4.3324 5.1731 2.8854
24 3,4-Dichloroaniline Training 162.02 3.3031 3.3448 3.0048
25 Dicyclohexylamine Training 181.32 4.4939 2.2432 2.8373
26 Diethylamine Training 73.14 4.9696 2.0318 2.6624
27 Diethyleneglycol Training 106.14 7.7059 3.6017 1.9352
28 N,N-Diethylmethylamine Training 87.16 4.8450 3.3448 3.0048
29 N,N-Diisopropylethylamine Training 129.25 5.0193 2.9621 2.8025
30 Diisobutylamine Training 129.3 4.6738 2.3816 2.6403
31 Diisopropylamine Training 101.2 4.9613 3.7035 3.1539
32 N,N-Dimethylamine Training 45.09 5.5985 5.4871 4.7149
33 N,N-Dimethylanilin Training 121.2 4.7342 1.1533 1.7563
34 N,N-Dimethylbutylamine Training 101.19 4.7075 0.7109 1.3753
35 N,N-Dimethylcyclohexylamine Training 127.23 4.7247 1.5988 1.7464
36 N,N-Dimethylethylamine Training 73.14 4.9183 5.1469 5.2986
37 N,N-Dimethylformamide Training 73.09 6.9746 4.8383 4.789
38 4,6-Dinitro-o-cresol Training 198.14 2.5910 4.5685 3.9195
39 2,4-Dinitrophenol Training 184.11 2.9542 2.4241 2.8188
40 Dipentylamine Training 157.3 4.6313 2.7028 2.7623
41 Dipropylamine Training 101.19 4.4936 2.4946 2.2544
42 Ethanol Training 46.1 7.0625 3.2158 4.2721
43 Ethylacetate Training 88.106 6.2692 2.9198 2.9311
44 Ethylenediamine Training 60.1 5.5984 3.5851 4.5713
45 1-Ethylpiperidine Training 113.2 4.8531 6.14 5.7386
46 2-Ethylpiperidine Training 113.2 4.9729 3.7661 2.8756
47 n-Heptylamine Training 115.22 4.4541 4.5401 4.1437
48 n-Hexylamine Training 101.19 4.6261 5.746 5.3312
49 Hydroquinone Training 110.11 3.8976 4.0228 4.1965
50 Hydroxyurea Training 76.05 6.2530 5.1664 5.3695
51 Isobutylamine Training 73.1 4.966694 4.201 4.4596
52 Isopentylamine Training 87.16 4.7715 2.315 2.1711
53 Isopropylamine Training 59.11 6.4425 2.6561 2.616
54 Methanol Training 32.04 7.3443 2.668 2.6086
55 Methoxyaceticacid Training 90.08 4.7298 4.6482 3.7387
56 2-Methoxyethanol Training 76.09 7.3125 1.4622 1.8345
57 1-Methoxy-2-propanol Training 90.12 7.1434 1.9533 2.2345
58 3-Methyl-1-butanol Training 88.17 6.0097 1.07 2.513
59 N-Methylamine Training 31.1 5.8525 2.0118 1.8028
60 N-Methylanilin Training 107.2 4.5339 3.1082 2.2898
61 N-Methylformamide Training 59.07 7.0408 1.2202 2.3192
62 1-Methylpiperidine Training 99.18 4.8346 2.956 2.9168
63 2-Methylpiperidine Training 99.18 5.0100 1.5135 1.2284
64 4-Methylpiperidine Training 99.18 4.9681 3.0818 2.47
65 Morpholine Training 87.12 5.7790 4.7142 5.0932
66 2-Nitroaniline Training 138.1 4.3324 2.3356 2.3419
67 4-Nitrobenzoicacid Training 167.12 4.4756 2.0638 2.3089
68 4-Nitrophenol Training 139.11 4.7573 1.2928 1.818
69 n-Nonylamine Training 143.27 4.0592 4.6492 2.7816
70 1-Octanol Training 130.23 4.18752 4.3523 5.4814
71 n-Octylamine Training 129.25 4.4058 0.5177 0.9196
72 Pentachlorophenol Training 266.34 2.7403 2.8802 2.3573
73 n-Pentylamine Training 87.16 4.4893 1.7798 1.2701
74 4-tert-Pentylphenol Training 164.24 3.5440 2.5337 1.7304
75 Phenol Training 94.11 5.3222 2.7298 2.5952
76 Piperidine Training 85.2 5.0433 3.9809 2.4011
77 2-Propanol Training 60.1 6.9721 5.3213 5.0889
78 n-Propylamine Training 59.11 4.8984 3.5419 2.5303
79 Salicylicacid Training 138.12 4.3577 4.8308 5.2073
80 Tetrachloroethylene Training 165.83 4.4281 2.8316 2.9567
81 2,4,6-Tribromophenol Training 330.8 3.6454 2.0737 2.352
82 Triethyleneglycol Training 150.2 7.7315 0.9536 2.5847
83 Urea Training 60.06 7.3598 2.354 2.2464
84 2,5-Hexanedion Test 114.14 6.6691 6.0191 5.6191
85 Acetone Test 58.08 4.0211 3.9211 3.0111
86 Acrolein Test 56 2.5682 1.9682 1.5682
87 Chloroacetaldehyde Test 78 3.5251 3.9551 2.9351
88 Diazinon Test 304.34 4.4961 4.1161 4.0161
89 Diethylene glycol dimethyl ether Test 134.18 7.0436 6.5236 7.9436
90 Dimethyl sulfoxide Test 78.13 7.4638 6.4638 6.1238
91 D-Mannitol Test 182.17 4.8908 5.0108 3.3508
92 Formamide Test 45.041 6.9610 7.0610 2.9210
93 p-tert-Butylphenol Test 150.22 3.2380 2.2380 1.2380
94 Quinone Test 108.09 2.6739 1.9739 0.6739
95 Saccharin sodium salt hydrate Test 241.2 7.3211 6.2111 8.11211
96 Tridecylmono-octylether Test 244.4 3.1568 2.1268 1.1128
97 Valproicacid Test 144.21 4.3051 3.9151 2.3751

Table 1: The experimental values of all compounds and the predicted LC50 by HM and SVM.

Development of linear model by SVM

The support vector machine algorithm was developed by Vapnik [17]. Support vector machine (SVM), as a novel type of learning machine is gaining rapid popularity due to its remarkable generalization performance [18], has gained much interest in pattern recognition and function approximation applications recently. In bioinformatics, SVMs have been successfully used to solve classification and correlation problems, with the basic idea of SVM is to map the original data into a higher dimensional feature space by a kernel function and then to do classification in this space by constructing an optimal separating hyperplane. Compared with traditional regression and neural networks methods, SVMs have some advantages, including the absence of local minima, good generalization ability, simple implementation, few free parameters, dimensional independence and its ability to condense information contained in the training set [19]. The flexibility in classification and ability to approximate continuous function make SVMs very suitable for QSAR and QSPR studies. Because it is difficult to predict in advance which descriptors are most relevant to the problem at hand, however, SVM is well known to tolerate irrelevant features [20-22]. In some cases, the best average performance was achieved when all the features were given to SVM [23].

Results And Discussion

Results of HM

The heuristic method is not made a prior choice of descriptors, but it performs an analysis on several intrinsic molecular properties available from the Gaussian output. We performed correlations for a growing number of descriptors in the range from 1 to 10.

Figure 1 shows the plots of R2, cross-validated coefficient (RCV 2) and the standard deviation (s2) for the training set as a function of the number of descriptors models. R2 and RCV 2 are increased with the increasing number of descriptors. However, the values of s2 decreased with the increasing number of descriptors [24,25]. When adding another descriptor did not improve significantly the statistics of a model, it was determined that the optimum subset size had been achieved. From Figure 1, it can be seen that six descriptors appear to be sufficient for a successful regression model. Then the corresponding descriptors are applied as inputs for the non-linear model.Best models were selected on the basis of their statistical significance. High r2 and high F and low s2 values in each model reflect their good predictive potential. Pair wise correlations between the descriptors used in the QSAR models obtained for series is summarized in Table 2. The molecular descriptors used in the selected QSAR models are defined in Table 3. The predict results are shown in Figure 2.

organic-chemistry-descriptors

Figure 1: Plot of R2/R2cv/s2 against the number of descriptors for logEC50 QSPR analysis.

organic-chemistry-toxicity

Figure 2: Predicted vs experimental toxicity by HM.

  A B C D E F
A 1.0000 -0.0725 0.2135 0.3806 0.4239 0.2161
B -0.0725 1.0000 -0.3540 -0.1499 -0.2106 0.1555
C 0.2135 -0.3540 1.0000 0.2619 0.1297 -0.2949
D 0.3806 -0.1499 0.2619 1.0000 0.2398 0.2922
E 0.4239 -0.2106 0.1297 0.2398 1.0000 -0.2729
F 0.2161 0.1555 -0.2949 0.2922 -0.2729 1.0000

Table 2: Correlation matrix of the six descriptors used in this work.

R2 R2CV F X+DX t-Test Descriptors
0.8142 0.7733 55.50 6.0388e+01 6.3153e+00 9.5622 Intercept(A)
      -1.3840e+01 1.5885e+00 -8.7129 Avgvalency of a C atom(B)
      -1.2775e+01 1.7259e+00 -7.4017 Relative number of double bonds(C)
      -1.9631e-02 2.5005e-03 -7.8508 Molecular volume(D)
      4.9342e-01 1.0389e-01 4.7492 HOMO-1 energy(E)
      -5.9297e-01 1.2477e-01 -4.7492 HOMO energy(F)
      -2.2411e+00 6.0338e-01 -3.7143 Average structural information content(order 1)(G)

1, Avg valency of a C atom;2, Relative number of double bonds;3, PPSA-3 Molecular volume;4, HOMO-1 energy;5, HOMO energy;6, Average Structural Information content (order 1);
The fitted regression model is: logEC50 = (6.0388e+01 6.3153e+00)*A+(- 1.3840e+01 1.5885e+00)*B+(-1.2775e+01 1.7259e+00)*C+(-1.9631e-02 2.5005e-03)*D+(4.9342e-01 1.0389e-01)*E+(-5.9295e-01 1.2477e-01)*F+(- 2.2411e+00 6.0338e-01)*G

Table 3: Correlations of toxicity by the heuristic method.

Results of SVM

SVM is a machine-learning approach that allows one to learn from experimental data within a given set, and build a computer model to make predictions on new data sets. The associated parameters are c, p and g, –t kernel function is the RBF kernel function: exp(- gamma*|uv|^2), the calculated optimal correlation parameters are c:3.9192, g:168.9664, p: 0.9892. The predict results are shown in Figure 3.

organic-chemistry-predicted

Figure 3: Predicted vs experimental toxicity by SVM.

Compare with the HM and SVM

In the HM method, the R2 and s2 are 0.8142 and 0.0380 in training set, the R2 and s2 are 0.9238 and 1.8503 in test set. At the same time, in the SVM method, the R2 and s2 are 0.7105 and 0.0604 in training set, the R2 and s2 are 0.7527 and 2.4351 in test set. The six descriptors are the most important physical chemistry properties for the construction of QSAR model for FET and the prediction of LC50 with satisfied results. The predicted results of either training set or test set of the HM are better than those of SVM, both in the R2 and s2. Therefore, the HM has a good generalized performance (Table 4) as a non-linear method.

  Training Test
R2 s2 R2 s2
HM 0.8142 0.0380 0.9238 1.8503
SVM 0.7105 0.0604 0.7527 2.4351

Table 4: Performance comparison between HM and SVM.

Unsaturated double bond, based on positive and negative regression coefficients, can be judged according to their contribution to the toxic compounds, The coefficients of number of double bonds is positive, the LC50 increase with the double bond value increases. As for the electron donation of the elide, it is noted that the HOMO energy can be used a new method for showing the basicity of elides. The descriptors that matter most is on the Highest Occupied Molecular Orbital (HOMO) calculated from quantum chemical calculation, which describes the effect of HOMO energies on the toxicity. The results also show that the contribution from the HOMO-1 becomes less important than HOMO. Molecular volume is important to toxicity, the information contained in high-resolution structural determination of macromolecules. The HOMO-1, which is lower in energy than the HOMO, features a large contribution for toxicity.

The HOMO of 4-Aminophenol, 2-Bromophenol, Butyldiglycol and 2-Propanol, were calculated by B3LYP/6-31G method. 2-Propanol was the highest toxicity with the highest HOMO, as well as 4-Aminophenol was the lowest toxicity with the lowest HOMO (Figure 4). The structure of 4-Aminophenol was similar to 2-Bromophenol. The toxicity 2-Bromophenol, with higher HOMO, was higher than 4-Aminophenol. The Highest Occupied Molecular Orbital (HOMO) describes the effect of HOMO energies on the toxicity.

organic-chemistry-predicted

Figure 4: Optimized cell structure for 4-Aminophenol, 2-Bromophenol, Butyldiglycol and 2-Propanol, using B3LYP/6-31G method of calculation.

Conclusion

A QSAR study for fish embryo toxicity test (FET) was performed using HM and SVM, based on electrostatic, CPSA, constitutional, and quantum-chemical descriptors and satisfactory results were obtained. Through analyzing the obtained results, the present study gives rise to QSAR with good statistical significance and predictive capacity. The 6-parameter model can be considered as the best linear modelthe correlations are satisfying. Additionally, HM produced good model with vigorous predictive ability. Furthermore, the proposed approach can also be extended in other QSAR investigations. Fish embryo testing of chemicals has matured to the point that international standardization, method validation, and broadening of chemical coverage is rapidly occurring. Fish embryo tests offer a reasonable alternative to increased use of fish in the future.

Acknowledgements

Financial support from 2013 Commonweal and Environmental Protection Project of Ministry of Environmental Protection of the People’s Republic of China(No.: 2013467028) and the National High Technology Research and Development Program of China(863 Program, No.: 2013AA06A308).

References

  1. EC (European Commission), 2007. Regulation ( EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the Registration, Evaluation, Authorization and Restriction of Che- micals (REACH), establishing a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC) No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council Directive 76/769/EEC and Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC. Off. J. Eur. Union L 136, 3–280.
  2. Braunbeck T, Boettcher M, Hollert H, Kosmehl T, Lammer E, et al. (2005) Towards an alternative for the acute fish LC(50) test in chemical assessment: the fish embryo toxicity test goes multi-species -- an update. ALTEX 22: 87-102.
  3. Yao XJ, Liu MC, Zhang XY (2002) Radial basis function network-based quantitative structure–property relationship for the prediction of Henry's law constant.Anal.aChim.Acta., ,462:101–117.
  4. Katritzky AR, Fara DC, Petrukhin RO, Tatham DB, Maran U, et al. (2002) The present utility and future potential for medicinal chemistry of QSAR/QSPR with whole molecule descriptors. Curr Top Med Chem 2: 1333-1356.
  5. Katritzky AR, Maran U, Lobanov VS, Karelson M (2000) Structurally Diverse Quantitative Structure-Property Relationship Correlations of Technologically Relevant Physical Properties. J ChemInfComputSci 4:1-18.
  6. Arning J, Stolte S, Baschen A, Stock F, Pitner WB, et al. (2008) Qualitative and quantitative structure activity relationships for the inhibitory effects of cationic head groups, functionalised side chains and anions of ionic liquids on acetylcholinesterase[J]. Green Chem10: 47–58.
  7. Katritzky AR, Lobanov VS, Karelson M (1995) CODESSA: Training Manual,University of Florida, Gainesville, FL.
  8. Katritzky AR, Lobanov VS, Karelson M (1994) CODESSA: Reference Manual,University of Florida, Gainesville, FL.
  9. Lammer E, Carr GJ, Wendler K, Rawlings JM, Belanger SE, et al. (2009) Is the fish embryo toxicity test (FET) with the zebrafish (Daniorerio) a potential alternative for the fish acute toxicity test? CompBiochemPhysiol C ToxicolPharmacol 149: 196-209.
  10. Kammann U, Vobach M, Wosniok W (2006) Toxic effects of brominated indoles and phenols on zebrafish embryos. Arch Environ ContamToxicol 51: 97-102.
  11. Frisch M J,Trucks G W,Schlegel H B, et al. (2003) Gaussian 03,revision A.1[K].Gaussian,Inc:Pittsburgh,PA.
  12. Eroglu E, Palaz S, Oltulu O, (2007) Comparative QSTR Study Using Semi-Empirical and First Principle Methods Based Descriptors for Acute Toxicity of Diverse Organic Compounds to the Fathead Minnow[J]. Int J MolSci 8:1265-1283.
  13. Katritzky AR, Lobanov VS, Karelson M(1994) CODESSA Reference Manual (version 2.0), Reference Manual, Version 2.0.
  14. Katritzky AR, Lobanov VS, KarelsonM  CODESSA: Reference Manual, University of Florida, Gainesville, FL.
  15. Devillers J, Chambon P (1986) Acute toxicity and QSAR of chlorophenols on Daphnia magna. Bull Environ ContamToxicol 37: 599-605.
  16. Katritzky AR, Petrukhin R, Jain R, Karelson M (2001) QSPR analysis of flash points. J ChemInfComputSci 41: 1521-1530.
  17. Liu HX, Zhang RS, Yao XJ, Liu MC, Hu ZD, et al. (2004) Prediction of the isoelectric point of an amino acid based on GA-PLS and SVMs. J ChemInfComputSci 44: 161-167.
  18. Chen C, Zhou X, Tian Y, Zou X, Cai P (2006) Predicting protein structural class with pseudo-amino acid composition and support vector machine fusion network. Anal Biochem 357: 116-121.
  19. Yang Y, Pederson JO (1995) A comparative study on feature selection in text categorization. In Fisher DH (ed): Proceedings of the ICML-95: 14th International Conference on Machine Leaning. San Francisco: Morgan Kaufmann: 412-420.
  20. Rogati M, Yang (2002) High-performing feature selection for text classification. In Proceedings of the 11th International Conference on Information and Knowledge Management. New York: ACM Press :659-661.
  21. Brank J, Grobelnik M, Milic-Frayling N, et al (2002) Interaction of feature selection methods and linear classification models. Proceedings of the ICML- 02 Workshop on Text Learning, Sydney, Australia.
  22. Taira H, Haruno M (1999) Feature selection in SVM text categorization. In Proceedings of the Sixteenth National Conference on Artificial Intelligence and the Eleventh Innovative Applications of Artificial Intelligence Conference. Menlo Park, CA: American Association for Artificial Intelligence: 480-486.
  23. Katritzky AR, Tatham DB, Maran U (2001) Theoretical descriptors for the correlation of aquatic toxicity of environmental pollutants by quantitative structure-toxicity relationships. J Chem Inf Comput Sci 41: 1162-1176.
  24. Bruzzone S, Chiappe C, Focardi SE (2011) Theoretical descriptor for the correlation of aquatic toxicity of ionic liquids by quantitative structure–toxicity relationships, Chem Eng J 175:17–23.
Citation: Jining L, Deling F, Lei W, Linjun Z, Lili S (2014) Theoretical Descriptor for the Correlation of the Fish Embryo Toxicity test (FET) By QSAR Model of LC50. Organic Chem Curr Res 3: 125.

Copyright: © 2014 Jining L, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Top