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1 te (pharmaceutical haloperidol and pesticide lindane).
2 rocyclohexane (gamma-HCH), commonly known as lindane.
3 thyl parathion and conjugates glutathione to lindane.
4 ere observed upon exposure to endosulfan and lindane.
5 -2) .d(-1)), CBzs (340 ng .m(-2) .d(-1)) and lindane (180 ng .m(-2) .d(-1)).
6 lly activated, and permethrin (190-fold) and lindane (63-fold), compounds acting, respectively, on so
7  The answer is that some of these compounds (lindane, alpha-HCH, and endosulfans) are well on their w
8       The rapid and selective degradation of lindane and concomitant generation of hydrochloric acid
9 and 69% and UV-aged adsorbed 9.7% and 63% of lindane and DDE, respectively) likely due to a shift in
10 igated the toxicity and bioaccumulation of a lindane and dichlorodiphenyldichloroethylene (DDE) mixtu
11 lture I and culture II, were responsible for lindane and MCB dechlorination, respectively.
12 gacy soil and groundwater contamination with lindane and other HCH isomers is still a big concern.
13 0mug/kg lipid) and, during the rainy season, Lindane and Sigma-HCH in muscle and lung samples from Pa
14 ing two organochlorine insecticides (DDT and lindane) and four herbicides (alachlor, metolachlor, 2,4
15  organochlorine pesticides aldrin, dieldrin, lindane, and alpha-endosulfan by using surface-enhanced
16 or insecticides, including alpha-endosulfan, lindane, and fipronil, and the botanical picrotoxinin ar
17  organochlorine pesticides such as p,p'-DDE, lindane, and hexachlorobenzene were found in higher conc
18                                          The lindane-biodegrading E. coli cells were immobilized on p
19 d with the dehydrochlorination of gamma-HCH (lindane) by two variants of the lindane dehydrochlorinas
20 For pesticides, no loss occurred for aldrin, lindane, DDE or DDD, whereas losses exceeding 80% were f
21 s of environmental factors, we conclude that lindane dechlorination by Anabaena sp. requires a functi
22                     Nitrate is essential for lindane dechlorination by the cyanobacteria Anabaena sp.
23  aromatic chlorides or to the end product of lindane degradation, i.e., trichlorobenzene (TCB).
24 f gamma-HCH (lindane) by two variants of the lindane dehydrochlorinases LinA1 and LinA2.
25 DT, etc.) versus soil mixing in rural areas (lindane, etc.).
26 nt 1) and by toxic exposure to the pesticide lindane (Experiment 2).
27                                           In lindane-exposed daphnids, a significant growth inhibitio
28 se (LinA2), involved in the initial steps of lindane (gamma-HCH) biotransformation, was cloned and ov
29 cal hexachlorocyclohexane (HCH) mixtures and Lindane (gamma-HCH) have been produced in Bitterfeld-Wol
30 ivity was developed for the determination of lindane, gamma-hexachlorocyclohexane (gamma-HCCH), based
31  persistent organochlorine (OC) insecticides lindane (HCH) and dieldrin (HEOD) to the development of
32                   The biosensor could detect lindane in the part-per-trillion concentration range wit
33 -evoked increase in [Ca(2+)](i), whereas the lindane-induced increase in basal [Ca(2+)](i) is inhibit
34 f hexachlorocyclohexane (HCH), also known as lindane, is a carcinogenic persistent organic pollutant.
35 ieldrin and a binary mixture of dieldrin and lindane on a critical parameter of neuronal function and
36 diazinon, DDT, hexachlorobenzene, iprodione, lindane, procymidone, and quintozene (1-460 ng/g).
37 e of PC12 cells to a mixture of dieldrin and lindane revealed an additive inhibition of the depolariz
38 on with culture I achieved dechlorination of lindane to MCB and benzene.
39  demonstrate that complete biodegradation of lindane to nontoxic end products is attainable using a s
40 the environmental contaminants methoxychlor, lindane, tributyltin chloride, pentachlorophenol, diuron
41                        The doses of DMSO and lindane used in these experiments are nontoxic and nonmu
42  coexposed with all particle types, although lindane was not detected in the cells.
43                                              Lindane was used worldwide as an agricultural insecticid
44                                              Lindane, which blocks gap-junctions, prevented the bysta
45     Treatment of cultured chick embryos with lindane, which diminishes gap junctional communication,
46 t, cells pretreated with a 40 microM dose of lindane, which inhibits cell-cell communication, signifi
47 scavenger DMSO or the gap junction inhibitor Lindane within the clusters significantly reduced the mu