Table 2.

IRRs of NHL in association with adipose tissue concentrations of organochlorine pesticides.

Compound/concentrationa (μg/kg lipids)	n (cases/subcohort)	IRR (95% CI)
		Model 1b	Model 2c
p,p´-DDT
6–15		29/37		1.00		1.00
15–22		32/32		1.09 (0.54, 2.18)		1.06 (0.52, 2.14)
22–36		35/38		1.12 (0.57, 2.19)		1.03 (0.51, 2.09)
36–49		23/19		1.25 (0.55, 2.80)		1.21 (0.53, 2.75)
49–460		18/11		1.73 (0.72, 4.14)		1.64 (0.68, 3.96)
Linear estimate per IQRd		137/137		1.36 (1.11, 1.68)		1.35 (1.10, 1.66)
p,p´-DDE
68–390		59/58		1.00		1.00
390–680		53/64		0.82 (0.49, 1.37)		0.83 (0.49, 1.39)
680–1,100		63/57		1.03 (0.62, 1.72)		1.04 (0.62, 1.73)
1,100–1,700		34/36		0.82 (0.45, 1.50)		0.79 (0.43, 1.46)
1,700–8,000		29/22		1.12 (0.58, 2.17)		1.10 (0.57, 2.14)
Linear estimate per IQRd		238/237		1.03 (0.86, 1.22)		1.02 (0.86, 1.22)
β-Hexachlorocyclohexane
15–45		50/60		1.00		1.00
45–57		50/54		1.15 (0.67, 1.99)		1.15 (0.66, 2.00)
57–77		61/58		1.27 (0.74, 2.17)		1.24 (0.72, 2.15)
77–96		38/25		1.59 (0.83, 3.03)		1.49 (0.76, 2.92)
96–370		26/23		1.06 (0.53, 2.11)		1.02 (0.50, 2.07)
Linear estimate per IQRd		225/220		0.99 (0.83, 1.17)		0.96 (0.81, 1.15)
cis-Nonachlor
3–5		30/50		1.00		1.00
5–7		35/42		1.23 (0.64, 2.35)		1.19 (0.61, 2.30)
7–10		42/32		1.56 (0.82, 2.96)		1.53 (0.80, 2.91)
10–15		27/21		1.64 (0.79, 3.41)		1.76 (0.84, 3.67)
15–39		21/11		2.60 (1.08, 6.27)		2.52 (1.04, 6.09)
Linear estimate per IQRd		155/156		1.13 (0.94, 1.36)		1.13 (0.94, 1.36)
trans-Nonachlor
6–25		47/67		1.00		1.00
25–33		53/52		1.33 (0.78, 2.28)		1.39 (0.81, 2.39)
33–46		65/60		1.40 (0.84, 2.36)		1.43 (0.85, 2.40)
46–62		41/33		1.37 (0.75, 2.52)		1.38 (0.75, 2.54)
62–290		29/20		1.60 (0.79, 3.24)		1.54 (0.76, 3.14)
Linear estimate per IQRd		235/232		1.03 (0.90, 1.18)		1.01 (0.89, 1.16)
Compound/concentrationa (μg/kg lipids)		n (cases/subcohort)		IRR (95% CI)
				Model 1b		Model 2c
Oxychlordane
8–19		30/52		1.00		1.00
19–25		38/46		1.31 (0.71, 2.43)		1.33 (0.72, 2.46)
25–33		46/39		1.87 (1.00, 3.49)		1.86 (1.00, 3.47)
33–41		34/18		2.81 (1.28, 6.14)		2.69 (1.22, 5.96)
41–354		21/16		1.95 (0.85, 4.46)		1.92 (0.84, 4.41)
Linear estimate per IQRd		169/171		1.13 (0.92, 1.40)		1.11 (0.89, 1.38)
Dieldrin
6–13		33/32		1.00		1.00
13–20		21/52		0.38 (0.19, 0.76)		0.36 (0.17, 0.73)
20–29		35/37		0.95 (0.49, 1.85)		0.91 (0.46, 1.79)
29–41		22/12		2.05 (0.92, 4.54)		1.94 (0.87, 4.34)
41–350		18/11		1.42 (0.60, 3.36)		1.27 (0.52, 3.12)
Linear estimate per IQRd		140/144		1.03 (0.94, 1.14)		1.03 (0.94, 1.13)
Hexachlorobenzene
9–37		47/56		1.00		1.00
37–53		50/51		1.08 (0.62, 1.88)		1.07 (0.61, 1.87)
53–72		45/56		0.84 (0.48, 1.49)		0.77 (0.42, 1.43)
72–98		37/33		1.15 (0.60, 2.18)		1.07 (0.55, 2.09)
98–360		25/17		1.25 (0.57, 2.72)		1.16 (0.53, 2.58)
Linear estimate per IQRd		204/213		1.00 (0.82, 1.21)		0.98 (0.80, 1.19)
ΣChlordanese
9–37		55/59		1.00		1.00
37–58		51/68		0.77 (0.46, 1.30)		0.75 (0.44, 1.27)
58–83		64/53		1.18 (0.70, 1.99)		1.10 (0.64, 1.91)
83–108		35/35		0.84 (0.45, 1.55)		0.80 (0.43, 1.50)
108–439		30/17		1.41 (0.68, 2.94)		1.32 (0.63, 2.79)
Linear estimate per IQRf		235/232		1.04 (0.86, 1.26)		1.02 (0.84, 1.24)
ΣDDTsg
76–390		57/56		1.00		1.00
390–690		57/67		0.86 (0.51, 1.43)		0.87 (0.52, 1.47)
690–1,100		61/56		1.02 (0.61, 1.72)		1.03 (0.61, 1.74)
1,100–1,714		36/37		0.86 (0.48, 1.56)		0.83 (0.46, 1.52)
1,714–8,041		27/21		1.09 (0.56, 2.15)		1.08 (0.55, 2.14)
Linear estimate per IQRh		238/237		1.03 (0.87, 1.23)		1.03 (0.86, 1.23)