• Nenhum resultado encontrado

Braz. J. Pharm. Sci. vol.48 número4

N/A
N/A
Protected

Academic year: 2018

Share "Braz. J. Pharm. Sci. vol.48 número4"

Copied!
2
0
0

Texto

(1)

Er

r

a

tu

m

Brazilian Journal of Pharmaceutical Sciences vol. 48, n. 4, oct./dec., 2012

v.48, n.3, 2012

- Page 513

Change the duplicated TABLE II for TABLE III as follow bellow or change the following reformulated page.

TABLE III - Classiication of waste in accordance with CONAMA resolutions No. 358 and ANVISA RDC 306

Group A Waste with the possible presence of biological agents. This group is subdivided into 5 classes: A1, A2, A3, A4 and A5.

Group B Waste containing chemical substances with lammable, corrosive, reactive and toxic characteristics.

Group C Material resulting from human activities that contain radionuclides in quantities greater than the limits.

Group D Waste that does not present risk, for example, domestic waste.

(2)

Critical analysis of the regulations regarding the disposal of medication waste 513

TABLE II - Classiication of waste

Class Classiication Description

Class I Hazardous Waste, which because of their physical, chemical or infecto-contagious properties, may present risks to public health. For example: products with lammable, corrosive, reactivity, toxicity and pathogenicity characteristics.

Class II Non-hazardous The non-hazardous waste was listed in the ABNT NBR 10.004.

Class II A Non-inert Those who do not it the classiications of Class I waste - Hazardous waste or class II B - inert. The residue class II - not inert may have properties such as biodegradability, combustibility or water solubility.

Class II B Inert Any residues that, when sampled in a representative and subjected to a dynamic and static contact with distilled or deionized water at room temperature, do not have any of its constituents dissolved concentrations exceed the standards of potable water, except for appearance, color, haze, hardness and lavor.

TABLE IV - Classiication of the types hazardous medication waste

Type 1 Hazardous medication that wasn’t used, was partially used, is expired or cannot be used

Hazardous medication originating from spills, as well as containment, absorption, removal and cleaning material contaminated by them

HEPA ilters from safety cabins where hazardous medication is handled

Infusion pockets and equipment, illed or partially used, and other non-empty containers containing solutions of hazardous medications over the established limits

Type 2 Empty containers, including primary packages, when they are completely empty (for example: bottles, vials, pill blisters) and equipment, utensils or disposable devices

Personal Protective Equipment originating from the handling and preparation of hazardous medications and routine activities

Surface, workbench and safety cabin liners that had no direct contact with hazardous medications

TABLE III - Classiication of waste in accordance with CONAMA resolutions No. 358 and ANVISA RDC 306

Group A Waste with the possible presence of biological agents. This group is subdivided into 5 classes: A1, A2, A3, A4 and A5.

Group B Waste containing chemical substances with lammable, corrosive, reactive and toxic characteristics.

Group C Material resulting from human activities that contain radionuclides in quantities greater than the limits.

Group D Waste that does not present risk, for example, domestic waste.

Group E Puncturing, cutting or scarifying materials, for example: needles, scalpel blades, lancets, micro-pipettes, pipettes, Petri dishes)

guarantee safety, minimizing environmental impacts

(Pinto et al., 2009).

Class I Hazardous Waste Landill: Technique for the disposal of chemical waste in the soil, using speciic engineering procedures for its coninement, without caus-ing damage or risk to public health and reduccaus-ing

environ-mental impact (Pinto et al., 2009).

The sanitary landill norms are dealt with especially by ABNT NBR norm No. 13.896, of July 30 of 1997, which deals with Non-hazardous waste landills – Criteria

for the project, implementation and operation; CONAMA RESOLUTION No. 313, of October 29, 2002 / ANNEX III, which Regulates the national industrial solid waste inventory; ABNT NBR 8418 and NBR 842 Abridgement on the Presentation of hazardous industrial waste landill projects and ABNT NBR 1057 and NBR 1025 Abridge-ment on the Hazardous waste landills – Criteria for the project, construction and operation.

Imagem

TABLE II  - Classiication of waste

Referências

Documentos relacionados

SS erythrocytes displayed increased rates of oxidation of hemoglobin and membrane lipid peroxidation compared to normal erythrocytes (HbAA, AA erythrocytes), and the concentration

Naproxen agglomerates were prepared by using a three solvents system composed of acetone (good solvent), water (non-solvent) and dichloromethane (bridging liquid)..

in refrigerated sausages, and to compare the performance of the selective plating media employed in the ISO 11290-1 method (PALCAM and Oxford agars) with chromogenic

luence of size and crystallinity of different lipid composi - tion in SLN formulations on the occlusion factor using in vitro method and the skin hydration using corneometer in

Triplicate samples of ceftazidime, aminophylline and the drug mixture were diluted in 5% glucose par- enteral solutions, followed by HPLC analysis at 0, 2, 6 and 24 h

In vitro release proile for formulations containing diltiazem HCl loaded BSA microparticles with heat stabilization technique shows slow controlled the release of the drug up to

The matrix effect was investigated using the following procedure: the luorescence intensity of the standard QC samples was compared to the luorescence intensity of AD in spiked

It is worth mentioning that in Brazil there is no legislation that limits the release of so-called emerging contaminants. Studies in Minas Gerais on the removal of