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. 2013 Nov 5;121(11-12):1319–1324. doi: 10.1289/ehp.1306648

Table 3.

Adjusted odds ratios (aORs) and 95% CIs for the relationship between individual organochlorine pesticides and endometriosis, Group Health, 1996–2001.

Pesticide quartiles (pg/g serum) All endometriosis Ovarian endometriosis
Case/control (n) aORa (95% CI) Case/control (n) aORa (95% CI)
β-HCH
≤ 26.99 49/126 1.0 17/126 1.0
> 26.99–43.06 41/127 0.8 (0.5, 1.4) 21/127 1.2 (0.5, 2.4)
> 43.06–74.01 78/127 1.7 (1.0, 2.8) 42/127 2.5 (1.2, 5.2)
> 74.01 64/127 1.3 (0.8, 2.4) 42/127 2.5 (1.1, 5.3)
γ-HCHb
≤ 10.0 (LOD) 129/295 1.0 69/295 1.0
> 10.0–13.89 54/112 1.1 (0.8, 1.7) 29/112 1.1 (0.7, 1.9)
> 13.89 61/112 1.3 (0.9, 1.9) 32/112 1.2 (0.7, 2.0)
∑HCH (mol/g serum)c
≤ 0.12 54/134 1.0 24/134 1.0
> 0.12–0.18 48/135 0.8 (0.5, 1.3) 21/135 0.8 (0.4, 1.7)
> 0.18–0.29 79/134 1.4 (0.9, 2.2) 45/134 1.8 (1.0, 3.3)
> 0.29 67/135 1.1 (0.6, 1.8) 42/135 1.6 (0.8, 3.0)
Heptachlor epoxide
≤ 17.10 40/110 1.0 21/110 1.0
> 17.10–26.19 55/110 1.4 (0.8, 2.4) 22/110 1.0 (0.5, 2.0)
> 26.19–42.91 59/110 1.4 (0.8, 2.3) 34/110 1.3 (0.7, 2.6)
> 42.91 51/109 1.2 (0.7, 2.1) 28/109 1.1 (0.5, 2.2)
Oxychlordane
≤ 28.31 52/124 1.0 24/124 1.0
> 28.31–51.96 46/125 0.8 (0.5, 1.3) 23/125 0.8 (0.4, 1.6)
> 51.96–79.55 57/126 1.0 (0.6, 1.6) 34/126 1.2 (0.6, 2.4)
> 79.55 73/124 1.2 (0.7, 2.1) 45/124 1.5 (0.8, 3.0)
trans-Nonachlor
≤ 51.37 55/134 1.0 21/134 1.0
> 51.37–75.15 55/135 1.0 (0.6, 1.6) 31/135 1.4 (0.7, 2.7)
> 75.15–107.65 56/134 1.0 (0.6, 1.6) 33/134 1.3 (0.7, 2.6)
> 107.65 82/135 1.4 (0.8, 2.4) 47/135 1.8 (0.9, 3.7)
∑Chlordane (mol/g serum)c
≤ 0.21 53/134 1.0 23/134 1.0
> 0.21–0.33 56/135 1.0 (0.6, 1.7) 24/135 1.0 (0.5, 1.9)
> 0.33–0.52 57/134 1.1 (0.6, 1.8) 36/134 1.5 (0.8, 2.9)
> 0.52 82/135 1.4 (0.8, 2.5) 49/135 1.8 (0.9, 3.7)
p,p′-DDE
≤ 905.86 55/134 1.0 25/134 1.0
> 905.86–1575.51 69/134 1.2 (0.8, 2.0) 38/134 1.4 (0.8, 2.6)
> 1575.51–2816.55 62/134 1.1 (0.7, 1.7) 31/134 1.1 (0.6, 2.1)
> 2816.55 61/135 1.0 (0.6, 1.7) 37/135 1.2 (0.6, 2.4)
p,p′-DDT
≤ 18.79 58/128 1.0 21/128 1.0
> 18.79–28.36 58/128 0.9 (0.6, 1.5) 33/128 1.4 (0.7, 2.6)
> 28.36–44.38 55/128 0.8 (0.5, 1.4) 32/128 1.2 (0.6, 2.3)
> 44.38 66/129 0.9 (0.6, 1.5) 38/129 1.3 (0.7, 2.6)
∑DDT (mol/g serum)c
≤ 2.88 55/135 1.0 25/135 1.0
> 2.88–5.03 71/134 1.3 (0.8, 2.0) 39/134 1.5 (0.8, 2.7)
> 5.03–8.95 59/135 1.0 (0.6, 1.7) 29/135 1.1 (0.6, 2.1)
> 8.95 63/134 1.1 (0.6, 1.8) 39/134 1.4 (0.7, 2.7)
Dieldrind
≤ 10.0 (LOD) 59/151 1.0 32/151 1.0
> 10.0–48.18 52/97 1.3 (0.8, 2.1) 17/97 0.7 (0.4, 1.5)
> 48.18–73.74 65/123 1.1 (0.7, 1.8) 39/123 1.2 (0.7, 2.1)
> 73.74 52/124 0.8 (0.5, 1.3) 30/124 0.8 (0.4, 1.4)
Hexachlorobenzene
≤ 159.74 49/135 1.0 23/135 1.0
> 159.74–278.998 71/134 1.4 (0.9, 2.1) 40/134 1.6 (0.9, 3.0)
> 278.998–589.30 72/134 1.4 (0.9, 2.1) 35/134 1.4 (0.7, 2.6)
> 589.30 56/135 0.9 (0.6, 1.5) 34/135 1.1 (0.6, 2.1)
Mirexb
≤ 10.0 (LOD) 133/320 1.0 68/320 1.0
> 10.0–15.47 45/97 1.1 (0.7, 1.8) 28/97 1.3 (0.8, 2.2)
> 15.47 60/98 1.5 (1.0, 2.2) 29/98 1.2 (0.7, 2.1)
aAdjusted for age, reference date year, smoking, alcohol, education, natural logarithm-transformed total lipids, and race/ethnicity. bLowest category consists of values < LOD. Middle and top categories, ≤ median or > median, based on observations with values among controls. cSummed chemicals used multiple imputation data (five data sets); quartile cut points and frequencies are from first imputed data set. dAll samples with values < LOD were categorized in the lowest category. Subsequent categories were created using the 50th and 75th percentile among the distribution in controls.