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1056

C

HANG

ET AL

.:

J

OURNAL OF

AOAC I

NTERNATIONAL

V

OL

.

99, N

O

.

4, 2016

ratios of predicted and measured results also have the relatively

higher deviation ratios of their initial values (10.1–13.7 ).

However, the deviation ratios of initial values of the other 14

pesticides were <10 , with a range of 0.1–9.1 . With the

decrease of the deviation ratio of initial values, the deviation

ratio of predicted and measured results gets smaller. It can

be concluded that the closer their initial values, the better the

results obtained.

Table 4. Deviation ratios of predicted and determined results of

c

concn at different time intervals

a

No.

Pesticide

Time interval, days

5

10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90

1

7ULÀXUDOLQ

13.3 14.1 11.6 í 21.0 15.4 14.1 18.0 11.6 16.0 í 17.8 10.0 19.2 11.4 21.5 20.3 20.2

2

7HÀXWKULQ

15.2 17.4 16.0 14.1 15.1 25.5 16.1 19.7 12.2 23.5 20.3 20.7 17.8 20.6 21.2 26.0 25.3 21.4

3

Pyrimethanil

5.4 11.2 9.7 3.6 3.5 7.7 6.2 9.0 0.3 11.1 6.6 8.8 6.3 11.7 10.4 20.0 13.7 14.1

4

Propyzamide 6.9 11.4 9.9 3.6 4.9 7.6 9.2 7.1 0.0 11.4 3.4 8.6 8.9 8.6 7.8 15.4 12.4 10.4

5

Pirimicarb

7.4 11.9 10.7 5.7 9.5 13.7 11.6 11.2 8.1 15.7 8.5 12.6 11.5 13.2 13.4 20.6 17.1 14.5

6

Dimethenamid 9.4 13.0 11.4 6.6 15.3 18.0 17.6 16.3 7.9 17.5 12.3 17.2 13.7 19.9 17.0 24.0 21.4 18.9

7

Fenchlorphos

6.5 12.8 11.3 í 9.2 12.8 4.1 12.0 8.0 13.9 3.8 15.6 16.0 17.7 12.7 24.4 19.3 18.5

8

Tolclofos-methyl

9.5 13.7 11.8 5.8 11.9 9.4 8.2 13.6 9.2 16.1 9.7 17.0 15.8 17.4 14.5 23.1 19.9 17.6

9

Pirimiphos-methyl

9.2 13.9 13.0 6.1 11.2 10.1 9.2 13.1 í 13.1 11.3 13.5 12.9 16.0 14.9 21.8 20.6 17.6

10

ƍ ''(

0.8 5.6 7.0 4.5 4.1 í 5.3 2.6 0.2 7.3 5.7 4.1 0.4 4.3 6.7 10.8 11.3 4.6

11 Bromophos-ethyl

3.8 10.5 10.8 2.4 8.0 1.2 5.6 6.0 5.7 10.5 3.4 11.6 9.2 13.2 10.7 17.8 16.8 12.4

12

ƍ ''(

0.4 5.2 6.4 3.9 3.5 í 4.5 1.8 í 6.4 5.4 4.5 0.4 5.2 7.9 10.8 11.4 5.6

13

Procymidone í

4.0 5.7 4.4 3.7 í 6.3 í í 4.8 2.0 3.9 í 1.9 6.2 9.8 8.6 2.9

14

Picoxystrobin í

2.7 5.5 4.0 2.5 í 8.4 í í 3.2 0.4 3.2 í 2.1 6.2 8.9 7.1 0.1

15

Quinoxyfen

2.3 11.2 10.1 4.1 1.2 í

8.1 í í 0.7 í 2.1 í 4.5 5.6 14.7 6.1 3.2

16

Chlorfenapyr

í

4.6 6.2 2.0 2.9 í 6.7 í í 3.1 í 3.7 í 2.3 4.0 8.4 6.0 í

17

Benalaxyl

í

4.2 4.6 4.0 3.0 í

6.8 í í 4.6 1.7 4.3 í 3.0 7.4 8.7 6.5 í

18

Bifenthrin

í

4.3 5.4 7.8 3.1 í 10.0 í í 3.5 4.2 4.7 í 3.7 8.9 11.1 7.8 í

19

'LÀXIHQLFDQ í

9.1 7.3 2.0 1.8 í

9.5 í í 0.5 í 2.3 í 4.7 6.6 13.5 8.2 2.5

20

Bromopropylate í

9.1 7.3 í 6.0 í 10.5 í í 2.1 í 4.5 í 10.0 6.9 10.2 7.4 0.3

a

9DOXHV DUH GHYLDWLRQ UDWLRV FDOFXODWHG DV GHWHUPLQHG UHVXOW í SUHGLFWHG YDOXH î · GHWHUPLQHG UHVXOW

Table 5. Initial values of

c

and

d

concns and the range of deviation ratios of predicted and determined results

No.

Pesticide

Initial value

Range of deviation

UDWLR

b

Revised range of deviation

UDWLR

c

c

&RQFQ ȝJ NJ

d

&RQFQ ȝJ NJ 'HYLDWLRQ UDWLR

a

1

7ULÀXUDOLQ

214.4

248.6

13.7

í WR

í WR

2

7HÀXWKULQ

106.1

122.6

13.5

12.2–26.0

12.2–25.5

3

Pyrimethanil

116.9

124.7

6.3

0.3–20.0

0.3–14.1

4

Propyzamide

119.6

126.6

5.5

0–15.4

0–12.4

5

Pirimicarb

114.7

126.2

9.1

5.7–20.6

5.7–17.1

6

Dimethenamid

46.2

51.9

11.1

6.6–24.0

6.6–21.4

7

Fenchlorphos

240.3

267.4

10.1

í WR

í WR

8

Tolclofos-methyl

116.7

130.5

10.5

5.8–23.1

5.8–19.9

9

Pirimiphos-methyl

113.0

126.3

10.6

í WR

í WR

10

ƍ ''(

451.7

466.9

3.3

í WR

í WR

11

Bromophos-ethyl

116.0

124.2

6.6

1.2–17.8

1.2–16.8

12

ƍ ''(

451.7

466.9

3.3

í WR

í WR

13

Procymidone

117.9

120.3

2.0

í WR

í WR

14

Picoxystrobin

234.0

236.0

0.9

í WR

í WR

15

Quinoxyfen

115.9

116.4

0.4

í WR

í WR

16

Chlorfenapyr

965.0

966.0

0.1

í WR

í WR

17

Benalaxyl

116.8

118.9

1.7

í WR

í WR

18

Bifenthrin

112.9

114.8

1.7

í WR

í WR

19

'LÀXIHQLFDQ

118.6

119.4

0.7

í WR

í WR

20

Bromopropylate

237.4

240.0

1.1

í WR

í WR

a

'HYLDWLRQ UDWLRV DUH FDOFXODWHG DV

d

&RQFQ í

c

FRQFQ î ·

d

concn.

b

%HWZHHQ SUHGLFWHG DQG GHWHUPLQHG UHVXOWV

c

%HWZHHQ SUHGLFWHG DQG GHWHUPLQHG UHVXOWV ZLWKRXW WKH GD\ LQWHUYDO UHVXOWV